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Diss Factsheets

Toxicological information

Genetic toxicity: in vivo

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Administrative data

Endpoint:
in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
Type of information:
experimental study
Adequacy of study:
key study
Study period:
From April 3, 2007 to August 7, 2007
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
2007
Report date:
2007

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
Deviations:
no
GLP compliance:
yes
Type of assay:
micronucleus assay

Test material

Constituent 1
Reference substance name:
4,4'-Isopropylidenediphenol, oligomeric reaction products with 1-chloro-2,3-epoxypropane, esters with acrylic acid
EC Number:
500-130-2
EC Name:
4,4'-Isopropylidenediphenol, oligomeric reaction products with 1-chloro-2,3-epoxypropane, esters with acrylic acid
Cas Number:
55818-57-0
Molecular formula:
Not applicable (UVCB substance)
IUPAC Name:
Reaction product of (4,4'-Isopropylidenediphenol, oligomeric reaction products with 1-chloro-2,3-epoxypropane) and 2-propenoic acid
Test material form:
liquid: viscous

Test animals

Species:
mouse
Strain:
other: CD-1® (ICR) BR
Sex:
male
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: Harlan, Frederick, USA
- Age at study initiation: 8 wk
- Weight at study initiation: Preliminary study: 32.9-39.4 g (males) or 25.8-29.4 g (females); Main study: 32.1-40.0 g (males)
- Assigned to test groups randomly: Yes, animals randomized using a computer program
- Housing: Individually housed in sanitary polycarbonate cages
- Diet (e.g. ad libitum): PMI Certified Rodent Diet® #5002, ad libitum
- Water (e.g. ad libitum): Tap water, ad libitum
- Acclimation period: 5 d

ENVIRONMENTAL CONDITIONS
- Temperature: 64-79 °F
- Humidity: 30-70%
- Air changes: 10/h
- Photoperiod: 12 h dark/12 h light

IN-LIFE DATES: From: April 12, 2007 To: April 19, 2007

Administration / exposure

Route of administration:
oral: gavage
Vehicle:
- Vehicle(s)/solvent(s) used: Corn oil
- Concentration of test material in vehicle: 25 or 50 mg/mL
- Amount of vehicle (if gavage): 20 mL/kg
- Lot/batch no. (if required): 12-455
- Source: Welch, Holme, & Clarke
- Storage: Refrigerated at 0-10 °C
Details on exposure:
PREPARATION OF DOSING SOLUTIONS: Test substance was emulsified with corn oil to give stock solution which was then diluted further to give the desired dose levels; formulations were held in a waterbath at ~60 to 70 °C prior to dosing and stirred during the dosing procedure to prevent emulsion breakdown.
Duration of treatment / exposure:
24 or 48 h
Frequency of treatment:
Once for dose levels of 500 and 1000 mg/kg bw, and twice, approximately 1 h apart, for the dose level of 2000 mg/kg bw (1000 mg/kg/dose, BID).
Doses / concentrationsopen allclose all
Remarks:
Doses / Concentrations:
500 mg/kg bw
Basis:
actual ingested
Remarks:
Doses / Concentrations:
1000 mg/kg bw
Basis:
actual ingested
Remarks:
Doses / Concentrations:
2000 mg/kg bw
Basis:
actual ingested
No. of animals per sex per dose:
-Range-finding study: 3 mice/sex/dose
-Main study: Five male mice/dose
Control animals:
yes, concurrent vehicle
Positive control(s):
Cyclophosphamide
- Lot no.: 076K1050
- Storage: Refrigerated at 0-10 °C
- Route of administration: Oral (gavage)
- Doses / concentrations: 80 mg/kg bw

Examinations

Tissues and cell types examined:
Hind limb bones (tibias) were removed for marrow extraction and the prepared slides were examined for polychromatic erythrocytes (PCEs), normochromatic erythrocytes (NCEs) and total erythrocytes.
Details of tissue and slide preparation:
CRITERIA FOR DOSE SELECTION: Dose selection was based on a preliminary range-finding test conducted on 3 mice/sex/dose at 500, 1000 and 2000 mg/kg bw. No mortality and/or toxic signs were recorded after 2 d of exposure.

TREATMENT AND SAMPLING TIMES: Hind limb bones (tibias) were removed for marrow extraction from five surviving animals in each treatment and control group at 24 or 48 h after exposure.

DETAILS OF SLIDE PREPARATION: Bone marrow cells extracted, preparations spread on slides and air-dried. The slides were fixed in methanol, stained with May-Grunwald solution and Giemsa and coded.

METHOD OF ANALYSIS: Slides were scanned to determine the frequency of micronuclei in 2000 polychromatic erythrocytes (PCEs) per animal. In addition, PCE:NCE ratio was determined in a population of 500 erythrocytes/animal.
Evaluation criteria:
- Criteria for a positive response: Detection of a statistically significant increase in micronucleated PCEs for at least one dose level, and a statistically significant dose-related response.
- Test substance that does not induce both of these responses is considered negative.
- Biological relevance of the results should be considered first.
Statistics:
- Statistical analysis was performed using ANOVA/Program Trend computer system.
- ANOVA followed by Dunnett’s t-test performed on untransformed proportions of cells with micronuclei per animal and on untransformed PCE:NCE ratios when the variances were homogeneous. Ranked proportions were used for heterogeneous variances.

Results and discussion

Test results
Key result
Sex:
male
Genotoxicity:
negative
Toxicity:
no effects
Vehicle controls validity:
valid
Negative controls validity:
not applicable
Positive controls validity:
valid
Additional information on results:
RESULTS OF RANGE-FINDING STUDY
- Dose range: 500-2000 mg/kg bw
- Solubility: Solubility limit in corn oil: 50 mg/mL
- Clinical signs of toxicity in test animals: No
- Evidence of cytotoxicity in tissue analyzed: Not examined
- Rationale for exposure: No appropriate toxicity data were available

RESULTS OF DEFINITIVE STUDY
- Frequency of micronuclei in polychromatic erythrocytes and PCE:NCE ratio: See table 1

Any other information on results incl. tables

Table 1: Micronucleus Assay - Summary Table

Treatment 

 Dose

 Harvest Time (h) 

% Micronucleated PCEs

Mean of 2000 per

Animal ± S.E.(Males)

Ratio PCE:NCE

Mean ± S.E.(Males)

 Controls 

 

 

 

 

 Vehicle 

 

 Corn Oil 20 mL/kg 

 

 24 

0.04 ± 0.02

0.51 ± 0.06

 48 

0.03 ± 0.02

0.35 ± 0.01

 Positive 

 CP 80 mg/kg bw

 24

2.77 ± 0.28* 

0.55 ± 0.1

 Test substance 

 

 

 

 500 mg/kg bw

 24

0.04 ± 0.03

0.43 ± 0.05

 1000 mg/kg bw

 24

0.06 ± 0.02

0.32 ± 0.07** 

 2000 mg/kg bwa 

 

 24

0.02 ± 0.01

0.59 ± 0.06

 48

0.05 ± 0.02

0.4 ± 0.08

* Significantly greater than the corresponding vehicle control, p ≤ 0.01.

** Significantly less than the corresponding vehicle control, p ≤ 0.05.

CP = Cyclophosphamide; PCE = Polychromatic erythrocyte; NCE = Normochromatic erythrocyte

aDue to solubility limit, the high dose was dosed at 1000 mg/kg BID (~1 h apart) to achieve a dose of 2000 mg/kg bw.

Applicant's summary and conclusion

Conclusions:
Under the test conditions, 'bisphenol A diglycidyl ether diacrylate' is not considered as mutagenic in an in vivo bone marrow micronucleus test.
Executive summary:

An in vivo bone marrow micronucleus test was performed with 'bisphenol A diglycidyl ether diacrylate' according to OECD Guideline 474, in compliance with GLP. CD-1® (ICR) BR male mice (5/dose) were given a single oral (gavage) dose of the test substance in corn oil at concentrations of 500 and 1000 mg/kg bw and twice, approx 1 h apart, at concentration of 2000 mg/kg bw (1000 mg/kg/dose, BID). Bone marrow was extracted after 24 or 48 h of exposure and the prepared slides were scanned to determine the frequency of micronuclei in 2000 polychromatic erythrocytes (PCEs) per animal. In addition, the number of PCEs and normochromatic erythrocytes (NCEs) in a population of 500 erythrocytes was determined as a measure of cytotoxicity. A preliminary range-finding test was also conducted on 3 mice/sex/dose at 500, 1000 and 2000 mg/kg bw and animals were observed for 2 d. In this previous test, no mortality and/or toxic signs were recorded. No statistically significant increases in the frequency of micronucleated PCEs were observed at any dose levels. A statistically significant decrease in the PCE:NCE ratios at a dose level of 1000 mg/kg bw was observed but was not considered biologically significant as the highest dose of 2000 mg/kg bw did not show a similar trend. Under the test conditions, the substance is not considered as mutagenic in an in vivo bone marrow micronucleus test (Yong, 2007).