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Diss Factsheets
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EC number: 944-271-1 | CAS number: -
- 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)
Genetic toxicity: in vivo
Administrative data
- Endpoint:
- in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2019
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
- Version / remarks:
- 2016
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of assay:
- mammalian erythrocyte micronucleus test
Test material
- Reference substance name:
- Reaction mass of (((1,3-phenylenebis(oxy))bis(ethane-2,1-diyl))bis(oxy))bis(ethane-2,1-diyl) bis(2-methylacrylate) and (1,3-phenylenebis(oxy))bis(propane-3,1-diyl) bis(2-methylacrylate) and 3-(3-(2-(2-(methacryloyloxy)ethoxy)ethoxy)phenoxy)propyl methacrylaterate
- EC Number:
- 944-271-1
- Cas Number:
- 2305048-54-6
- Molecular formula:
- not applicable for multi-constituent.
- IUPAC Name:
- Reaction mass of (((1,3-phenylenebis(oxy))bis(ethane-2,1-diyl))bis(oxy))bis(ethane-2,1-diyl) bis(2-methylacrylate) and (1,3-phenylenebis(oxy))bis(propane-3,1-diyl) bis(2-methylacrylate) and 3-(3-(2-(2-(methacryloyloxy)ethoxy)ethoxy)phenoxy)propyl methacrylaterate
Constituent 1
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source (i.e. manufacturer or supplier) and lot/batch number of test material: 3M Company, Batch 653940
- Purity, including information on contaminants, isomers, etc.: 100% (per Protocol)
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Room temperature, protected from light
- Stability and homogeneity of the test material in the vehicle/solvent under test conditions (e.g. in the exposure medium) and during storage: No data
- Stability in the medium, i.e. sensitivity of the test material to hydrolysis and/or photolysis: No data
- Solubility and stability of the test material in the solvent/vehicle and the exposure medium: No data
- Reactivity of the test material with the incubation material used (e.g. plastic ware): No data
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing (e.g. warming, grinding): None, test article was administered unchanged.
- Preliminary purification step (if any): No data
FORM AS APPLIED IN THE TEST (if different from that of starting material) : Unchanged
Test animals
- Species:
- mouse
- Strain:
- CD-1
- Details on species / strain selection:
- Test system recommended per OECD 474.
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Envigo RMS, Inc., Frederick, MD
- Age at study initiation: 7 weeks
- Weight at study initiation: 30.6-35.3 g
- Assigned to test groups randomly: Yes, randomization procedure within Microsoft Excel
- Fasting period before study: No data
- Housing: See below
- Diet (e.g. ad libitum): ad libitum
- Water (e.g. ad libitum): ad libitum
- Acclimation period: 7 days
ENVIRONMENTAL CONDITIONS
- Temperature: 72°F
- Humidity (%): 50
- Air changes (per hr): 10
- Photoperiod (hrs dark / hrs light): No data
Administration / exposure
- Route of administration:
- oral: gavage
- Vehicle:
- None
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: None, dosed neat.
- Duration of treatment / exposure:
- Exposed once
- Frequency of treatment:
- Exposed once
Doses / concentrationsopen allclose all
- Dose / conc.:
- 0 mg/kg diet
- Dose / conc.:
- 500 mg/kg diet
- Remarks:
- equivalent to 0.35 mL/kg
- Dose / conc.:
- 1 000 mg/kg diet
- Remarks:
- equivalent to 0.69 mL/kg
- Dose / conc.:
- 2 000 mg/kg diet
- Remarks:
- equivalent to 1.39 mL/kg
- No. of animals per sex per dose:
- 6
- Control animals:
- yes, concurrent no treatment
- Positive control(s):
- Cyclophosphamide (CP)
- Justification for choice of positive control(s): Per OECD 474
- Route of administration: Oral gavage
- Doses / concentrations: 50 mg/kg
Examinations
- Tissues and cell types examined:
- Polychromatic erythrocytes (PCE)
- Details of tissue and slide preparation:
- CRITERIA FOR DOSE SELECTION: Based on a dose range-finding study.
TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields): 24 and 48 hours after treatment
DETAILS OF SLIDE PREPARATION: Cells were re-suspended and a small drop of the bone marrow suspension was spread onto a clean glass slide. Four slides were prepared from each animal, air dried and fixed by dipping in methanol. One set of two slides (including 5 positive control slides) were stained with acridine orange for microscopic evaluation. The other set of slides was kept as backup and were archived. Each slide was identified by the harvest date, study number, and animal number (or slide number for positive control slides). Slides were coded using a random number table by an individual not involved with the scoring process.
METHOD OF ANALYSIS: The criteria for the identification of micronuclei are those of Schmid (1975). Micronuclei are brightly stained bodies that generally are round and that generally are between 1/20 and 1/5 the size of the PCE. Scoring was based upon the micronucleated cell, not the micronucleus; thus, occasional cells with more than one micronucleus were counted as one micronucleated PCE (MnPCE), not two (or more) micronuclei.
OTHER: 4000 PCE/animal - Evaluation criteria:
- A test article was considered to have induced a positive response if:
a) at least one of the test article doses exhibited a statistically significant increase when compared with the concurrent negative control (p ≤ 0.05), and
b) when multiple doses were examined at a particular sampling time, the increase was dose-related (p ≤ 0.01 and R2≥70%), and
c) results of the group mean or of the individual animals in at least one group were outside the 95% control limit of the historical negative control data.
A test article was considered to have induced a clear negative response if none of the criteria for a positive response were met and there was evidence that the bone marrow was exposed to the test article (unless intravenous administration was used). - Statistics:
- Statistical analysis was performed on the micronucleus frequency (%MnPCE) and %PCE
using the animal as the unit. The mean and standard deviation of %MnPCE and %PCE were
presented for each treatment group.
The use of parametric or non-parametric statistical methods in the evaluation of data was
based on the variation between groups. The group variances for micronucleus frequency for
the untreated and test article groups at the respective sampling time were compared using
Levene’s test (significant level of p less than or equal to 0.05). Since the variation between groups was found
not to be significant; a parametric one-way ANOVA was performed followed by a Dunnett’s
post-hoc analysis to compare each dose group to the concurrent untreated control.
A linear regression analysis was conducted to assess dose responsiveness in the test article
treated groups (p less than or equal to 0.01 and R2 ≥ 70%).
A pair-wise comparison (Student’s T-test; p less than or equal to 0.05) was used to compare the positive control
group to the concurrent untreated control group.
Results and discussion
Test results
- Key result
- Sex:
- male
- Genotoxicity:
- negative
- Toxicity:
- no effects
- Vehicle controls validity:
- not applicable
- Negative controls validity:
- not examined
- Positive controls validity:
- valid
- Additional information on results:
- RESULTS OF RANGE-FINDING STUDY
- Dose range: 2000 mg/kg
- Rationale for exposure: limit dose as recommended by guideline
RESULTS OF DEFINITIVE STUDY
- Induction of micronuclei (for Micronucleus assay): No statistically significant increase in the incidence of MnPCEs was observed in the test article treated groups relative to the untreated group at either time point (24 or 48 hours).
- Ratio of PCE/NCE (for Micronucleus assay): No appreciable reductions in the PCE/EC ratio were observed in the test article groups compared to the untreated group, indicating the test article did not induce cytotoxicity.
- Appropriateness of dose levels and route: As recommended by guideline
- Statistical evaluation: Statistical analysis was performed on the micronucleus frequency (%MnPCE) and %PCE using the animal as the unit. The mean and standard deviation of %MnPCE and %PCE were presented for each treatment group. The use of parametric or non-parametric statistical methods in the evaluation of data was based on the variation between groups. The group variances for micronucleus frequency for the untreated and test article groups at the respective sampling time were compared using Levene’s test (significant level of p < 0.05). Since the variation between groups was found not to be significant; a parametric one-way ANOVA was performed followed by a Dunnett’s post-hoc analysis to compare each dose group to the concurrent untreated control. A linear regression analysis was conducted to assess dose responsiveness in the test article treated groups (p< 0.01 and R2 ≥ 70%). A pair-wise comparison (Student’s T-test; p < 0.05) was used to compare the positive control group to the concurrent untreated control group.
Applicant's summary and conclusion
- Conclusions:
- Based on the increased plasma bromine concentrations following dosing, the test article was absorbed and distributed to the body and therefore the bone marrow was properly exposed. No significant increase in the presence of micronuleated polychromatic erythrocytes (MnPCEs) was observed in any group indicating that DiBrORMA is negative in the mouse micronucleus assay.
- Executive summary:
The test article, DiBrorma, was evaluated for its clastogenic activity and/or disruption of the mitotic apparatus by detecting micronuclei in polychromatic erythrocytes (PCEs) in mouse bone marrow in a GLP-compliant study conducted according to OECD Guideline 474 (2016). CD-1 mice (6 males/group at 24 hoursand an additional 6 males in the high dose and control groups at 48 hours) received 0 (untreated), 500, 1000, or 2000 mg/kg of undiluted DiBrORMA via single oral gavage. Blood was collected from 3 animals/timepoint at 1 hour (control only), 2, 4, 8, and 24 hours post-dose.The mice were euthanized at 24 hours or 48 hours post-dose as indicated above.The collected plasma samples were evaluated for the presence of bromine following a digestion step to release any covalently bound bromine (i.e., bromine bound in the test article compound or its metabolites). No significant increase in the presence of micronuleated polychromatic erythrocytes (MnPCEs) was observed in any group. Plasma bromine concentrations were increased following treatment with DiBrORMA while the concentration in the control group was approximately 2.4 ug/mL.The highest individual peak concentrations (Cmax) were 36.2, 58.9, and 57.6 ug/mL for the 500, 1000, and 2000 mg/kg groups, respectively, at 2, 4, and 2 hours post-dose, respectively (Tmax). At 24 hours post-dose,the mean plasma bromine concentrations had decreased to 6.1, 5.1, and 10.4 ug/mL for the 500, 1000, and 2000 mg/kg groups, respectively. Based on the increased plasma bromine concentrations following dosing, the test article was absorbed and distributed to the body and therefore the bone marrow was properly exposed.
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