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Diss Factsheets

Administrative data

Endpoint:
in vivo mammalian somatic cell study: cytogenicity / erythrocyte micronucleus
Remarks:
Type of genotoxicity: chromosome aberration
Type of information:
experimental study
Adequacy of study:
key study
Study period:
1986
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: Renowned laboratory following protocol equivalent to OECD guideline

Data source

Referenceopen allclose all

Reference Type:
publication
Title:
Inactivity of glycerol formal in a mouse micronucleus assay: relationship to its teratogenicity
Author:
Ashby J. & Ratpan F.
Year:
1986
Bibliographic source:
Environmental Mutagenesis, 8: 873-877
Reference Type:
publication
Title:
Evaluation of some formaldehyde-release compounds and other biocides in the mouse micronucleus test
Author:
Richardson C.R., Styles J.A. & Burlinson B.
Year:
1983
Bibliographic source:
Mutation Research, 124: 241-246

Materials and methods

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

Test material

Constituent 1
Reference substance name:
Glycerol formal
IUPAC Name:
Glycerol formal
Details on test material:
Glycerol formal was purchased from Lancaster Synthesis Limited, Morcambe, UK and was providedas a mixture of 1,2- and 1,3-acetal in 1:3 ratio.

Test animals

Species:
mouse
Strain:
C57BL
Sex:
male/female
Details on test animals or test system and environmental conditions:
TEST ANIMALS
- Source: not specified
- Age at study initiation: 6-8 weeks
- Weight at study initiation: not specified
- Assigned to test groups randomly: [no/yes, under following basis: ]
- Fasting period before study:
- Housing: 5 per cage
- Diet (e.g. ad libitum): Porton Combined Diet supplied by BP Nutrition Ltd., Stepfield, Whitam, Essex, Great Britain, ad libitum
- Water (e.g. ad libitum): water ad libitum
- Acclimation period: not specified

ENVIRONMENTAL CONDITIONS
- Temperature (°C): 20-22
- Humidity (%): 29-58
- Air changes (per hr): not specified
- Photoperiod (hrs dark / hrs light): 12/12

IN-LIFE DATES: not specified

Administration / exposure

Route of administration:
oral: gavage
Vehicle:
None
- Vehicle(s)/solvent(s) used: corn oil
Details on exposure:
Not specified
Duration of treatment / exposure:
24 and 48h
Frequency of treatment:
daily
Post exposure period:
None
Doses / concentrationsopen allclose all
Remarks:
Doses / Concentrations:
1870 and 3000 mg/kg
Basis:
nominal conc.
For males and females in the First study
Remarks:
Doses / Concentrations:
1620 and 2600 mg/kg
Basis:
nominal conc.
For males in the Second study
Remarks:
Doses / Concentrations:
3125 and 5000 mg/kg
Basis:
nominal conc.
For females in the Second study
No. of animals per sex per dose:
5
Control animals:
yes, concurrent vehicle
Positive control(s):
cyclophosphamide
- Route of administration: oral gavage
- Doses / concentrations: 10 ml/kg

Examinations

Tissues and cell types examined:
Bone marrows
Details of tissue and slide preparation:
CRITERIA FOR DOSE SELECTION:
In STUDY 1, mice were treated with 80 and 50% of the 7-day maximum tolerated dose (MTD-7) level as a single gavage bolus in corn oil. Due to the high toxicity of these doses towards males, a more accurate determination of the MTD-7 was made separately for males and females in STUDY 2.

TREATMENT AND SAMPLING TIMES ( in addition to information in specific fields):
A AJOUTER

DETAILS OF SLIDE PREPARATION:
Bone marrow smears were prepared using the paintbrush technique, 24 and 48 hours after a single gavage dose of the test chemical or the positive control agent. Slides were stained with Giemsa and read blind, 1000 polychromatic erythrocytes (PE) being assessed for micronucleated polychromatic erythrocytes (MPE) per animal.

METHOD OF ANALYSIS:
In STUDY 1, cells for assessment were selected from areas of slide rich in PE. As a re-analysis, selected slides from the first study were reassessed for the incidence of MPE. This involved assessment of 10000 PE per slide, reading in continuous fields accross the smear, starting from the beginning of the smear.
In STUDTY 2, 1000 PE were assessed for MPE, starting at the beginning of the smear.
These different methods of slide assessment were due to changes made to Central Toxicology Laboratory test protocol.

Evaluation criteria:
Statistics were the only criteria used to evaluate GF clastogenicity.
Statistics:
Differences between control and treated groups were assessed using single-sided Students t-test

Results and discussion

Test results
Sex:
male/female
Genotoxicity:
negative
Toxicity:
yes
Remarks:
Only mortality was recoded (number of surviving animals/initial number of animals). For males: 4/5 at 1870 mg/kg at 24h sampling; 0/5 at 3000 mg/kg at 24h sampling; 2/5 at 3000 mg/kg at 48h sampling; 4/5 at 1620 mg/kg at 24h and 48h. For females: 4/5 at 1
Vehicle controls validity:
valid
Negative controls validity:
not examined
Positive controls validity:
valid
Additional information on results:
FIRST STUDY
Mice were treated with GF at 1870 and 3000 mg/kg. As shown in Table 1 (in "Any other information on results incl. tables"), these dose levels were too much toxic to males.

SECOND STUDY
Due to toxicity met in first study, revised dose levels were employed.

Both studie showed no evidence of clastogenic response of GF. The inactivity of GF was confirmed when selected slides from the first study were assessed more extensively (using 10000 PE rather than 1000 PE) as shown in Table 3.

Statistical evaluation
No statistically significant differences were established between vehicle control and GF treatments groups whereas statistically significant differences were established between vehicle control and cyclophosphamide positive control groups (p < 0.001), using a single-sided Studentst-test (Tables 1 and 2).

Any other information on results incl. tables

Table 1: Incidence of Micronucleated Polychromatic Erythrocytes (MPE) per 1000 Polychromatic Erythrocytes (PE) at the 2 sampling times shown for glycerol formal (GF), corn oil and cyclophosphamide (CP)

 

Treatment

MPE/ 1000 PE ± SD (number of animals)

24 h sampling

48 h sampling

Male

Female

Male

Female

Corn oil (10 ml/kg)

3.80 ± 1.1 (5)

2.0 ± 1 (5)

3.80 ± 2.1 (5)

2.20 ± 1.3 (5)

CP (65 mg/kg)

33.20 ± 5.8* (5)

29.80 ± 3.03* (5)

23.0 ± 0.9 (5)

15.20 ± 2.3* (5)

GF (1870 mg/kg)

1.75 ± 0.96 (4)

1.75 ± 0.5 (4)

3.40 ± 0.9 (5)

1.50 ± 1.0 (5)

GF (3000 mg/kg)

-         (0)

2.50 ± 1.3 (4)

3.50 (2)

2.80 ± 1.5 (5)

*Statistically significantly different from controls, p <0.001 (single-sided Student t-test)

 

Table 2: Incidence of MPE/ 1000 PE at the 2 sampling times shown for glycerol formal (GF), corn oil and cyclophosphamide (CP)

 

Treatment

MPE/ 1000 PE ± SD (number of animals)

24 h sampling

48 h sampling

24 hr/48 h male/female (comnined)

Male

Female

Male

Female

Corn oil (10 ml/kg)

2.4 ± 1.1 (5)

1.2 ± 1.3 (5)

1.4 ± 1.1 (5)

1.2 ± 0.8 (5)

1.55 ± 1.14 (20)

CP (65 mg/kg)

13.2 ± 1.5* (5)

10.0 ± 1* (5)

15.4 ± 1.9 (5)

10.2 ± 1.8* (5)

13.7 ± 4.2* (20)

GF (1870 mg/kg)

1.25 ± 0.96 (4)

 

2.4 ± 0.56 (4)

 

1.34 ± 1.14 (18)

GF (3000 mg/kg)

 

0.75 ± 0.96 (5)

 

0.8 ± 1.1 (5)

GF (3000 mg/kg)

2.2 ± 0.84 (5)

 

1.8 ± 1.6 (5)

 

1.35 ± 1.34 (20)

GF (3000 mg/kg)

-          

1.0 ± 1 (5)

 

0.2 ± 0.45 (5)

*Statistically significantly different from controls, p <0.001 (single-sided Student t-test)

 

Table 3: Results of re-analysing selected slides from animals included in Table 1, such that 10 000 PE, instead of 1000 PE, were assessed per slide

 

Test group

MPE/ 1000 PE

Original values (1000 PE)

Original mean ± SD

Values from extended assessment (10 000 PE)

Final mean ± SD

48h, female, vehicle control

4, 1, 2

2.3 ± 1.5

1.6, 1.4, 2.0

1.7 ± 0.3

48h, male, vehicle control

6, 2.6

4.7 ± 2.3

3.3, 2.9, 3.5

3.2 ± 0.3

48h, male, CP

31

 

18.8

 

48h, male, GF

4, 4, 4

4 ± 0

3.5, 2.5, 2.7

2.90 ± 0.5

Applicant's summary and conclusion

Conclusions:
Interpretation of results (migrated information): negative
The mammalian erythrocyte micronucleus test showed no evidence of a clastogenic response of glycerol formal.
Executive summary:

The mammalian erythrocyte micronucleus test was performed on mice C57BL in 2 times to identify clastogenic potential of glycerol formal (GF).

In the first study, male and female mice were treated with GF at 1870 and 3000 mg/kg by oral gavage route (single dose). Due to high GF toxicity towards males, a second study was performed with the following concentrations in GF: 1620 and 2600 mg/kg for males and 3125 and 5000 mg/kg for females. In both studies, corn oil (at 10 ml/kg) and cyclophosphamide (at 65 mg/kg) were used as vehicle and positive control, respectively respectively

Number of Micronucleated Polychromatic Erythrocytes (MPE) per 1000 Polychromatic Erythrocytes (PE) were assessd at 24- and 48 -hour sampling.

In both studies, no statistically significant differences were established between vehicle control and GF treatments groups whereas statistically significant differences were established between vehicle control and cyclophosphamide positive control groups (p < 0.001), using a single-sided Studentst-test (Tables 1 and 2).

The mammalian erythrocyte micronucleus test showed no evidence of a clastogenic response of glycerol formal.