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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 / bone marrow chromosome aberration
Type of information:
experimental study
Adequacy of study:
key study
Study period:
1990-02-06 to 1990-05-23
Reliability:
1 (reliable without restriction)
Rationale for reliability incl. deficiencies:
guideline study

Data source

Reference
Reference Type:
study report
Title:
Unnamed
Year:
1990
Report date:
1990

Materials and methods

Test guideline
Qualifier:
according to guideline
Guideline:
OECD Guideline 474 (Mammalian Erythrocyte Micronucleus Test)
GLP compliance:
yes
Type of assay:
mammalian erythrocyte micronucleus test

Test material

Constituent 1
Chemical structure
Reference substance name:
Phenol
EC Number:
203-632-7
EC Name:
Phenol
Cas Number:
108-95-2
Molecular formula:
C6H6O
IUPAC Name:
phenol
Constituent 2
Reference substance name:
1-chlorododecane
Molecular formula:
C12H25Cl
IUPAC Name:
1-chlorododecane
Constituent 3
Reference substance name:
1-Dodecanol
Cas Number:
112-53-8
Molecular formula:
C12H26O
IUPAC Name:
1-Dodecanol
Constituent 4
Reference substance name:
1-Tetradecanol
Cas Number:
112-72-1
Molecular formula:
C14H30O
IUPAC Name:
1-Tetradecanol
Constituent 5
Reference substance name:
triphenyl phosphate
Cas Number:
115-86-6
Molecular formula:
C18H15O4P
IUPAC Name:
triphenyl phosphate
Constituent 6
Chemical structure
Reference substance name:
-
EC Number:
431-760-5
EC Name:
-
Cas Number:
27460-02-2
Molecular formula:
C24H35O4P
IUPAC Name:
dodecyl diphenyl phosphate
Constituent 7
Chemical structure
Reference substance name:
diphenyl tetradecyl phosphate
Cas Number:
142474-86-0
Molecular formula:
C26H39O4P
IUPAC Name:
diphenyl tetradecyl phosphate
Constituent 8
Reference substance name:
Didodecyl phenyl phosphate
Cas Number:
56827-93-1
Molecular formula:
C30H55O4P
IUPAC Name:
Didodecyl phenyl phosphate
Test material form:
liquid

Test animals

Species:
mouse
Strain:
CD-1
Sex:
male/female
Details on test animals or test system and environmental conditions:
Male and female CD-1 mice. Upon receipt, the animals were quarantined for nine days. Only animals considered healthy by a staff veterinarian were released from quarantine and used for testing.
Prior to testing, the mice were uniquely identified using ear tags and corresponding cage cards.
The animals were housed two per cage prior to dosing and subsequently one per cage after dosing. The animals were housed in stainless steel cages with stainless steel mesh bottoms.
Water was provided ad libitum via an automatic watering system. Purina Certified Laboratory Rodent Chow No. 5002 was used as the diet and was nutritionally acceptable for the maintenance of laboratory rodents and has been certified by the manufacturer not to contain contaminants likely to interfere with the study.
The animals were housed in rooms designed to routinely maintain a 12-hour light cycle, a temperature between 64 and 79 °F, and humidity between 40 and 70%. There were no excursions in animal room environmental conditions which had any obvious impact on the results of the study.

Administration / exposure

Route of administration:
intraperitoneal
Vehicle:
Solutions of the test material were made using corn oil as the solvent on the day of treatment
Doses / concentrationsopen allclose all
Dose / conc.:
500 mg/kg bw/day (nominal)
Dose / conc.:
2 500 mg/kg bw/day (nominal)
Dose / conc.:
5 000 mg/kg bw/day (nominal)
No. of animals per sex per dose:
15 mice / sex / dose (5 mice / sex for positive control)
Control animals:
not specified
Positive control(s):
Cyclophosphamide (60 mg/kg) was used as the positive control

Examinations

Tissues and cell types examined:
bone marrow cells
Details of tissue and slide preparation:
All animals were sacrificed by cervical dislocation and their femora were removed. Each bone was opened at the end and the bone marrow was flushed into approx. 2 ml of fetal bovine serum in a centrifuged tube. Bone marrow from both femora of each animal were pooled for slide preparation. The suspension was centrifuged to remove the serum. A portion of the remaining cells was placed on a clean glass microscope slide and a smear were prepared. Following preparation of the smears the slides were allowed to air dry overnight. The slides were stained using a Hema-Tek II slide staining machine and a Wright-Giemsa Stain Pak which includes stain, buffer and rinse solution.
Evaluation criteria:
Micronuclei were identified as uniform, darkly stained, round or oval shaped bodies found in the cytoplasm of polychromatic erythrocytes (PCEs). Bodies in PCEs which are refractile, improperly shaped or stained, or which were not in the focal plane of the cell were not scored as micronuclei. Cells containing more than one micronucleus were scored as a single micronucleated cell. The number of micronucleated PCEs per 1000 PCEs and the number of PCEs and normochromatic erythrocytes (NCEs) per 1000 erythrocytes was determined for each animal.
Statistics:
The individual test animal was used as the individual unit for analysis of micronucleated PCE frequency and PCE/erythrocyte fraction. Micronucleated PCE frequencies observed for each animal were transformed as the square root prior to analysis. PCR/total erythrocyte fractions were not transformed. A Dunnent’s test (one sided) was used for comparison of treatment group and positive control values which solvent control values. A significance level of p<0.05was used.

Results and discussion

Test results
Key result
Sex:
male/female
Genotoxicity:
negative
Toxicity:
no effects
Vehicle controls validity:
valid
Negative controls validity:
not examined
Positive controls validity:
valid
Remarks on result:
not determinable

Any other information on results incl. tables

Summary of micronucleus assay results for XP-2563 mean body weight change and animal observations

Dosage (mg/kg)

Sex

Number treated

Mean body weight change (g)±sd

Deaths

Observations

24 hours

48 hours

72 hours

Corn oil (control)

Male

15

-0.9±0.5

-1.0± 0.4

-0.5± 0.2

0

Normal

Female

15

-0.8± 1.1

-1.4± 0.6

-0.6± 0.9

0

Normal

500

Male

15

-3.3± 4.2

-1.9± 0.5

-1.7± 0.7

0

Normal

Female

15

-0.7± 1.0

-1.6± 0.8

-1.4± 0.6

0

Normal

2500

Male

15

-2.2± 0.3 **

-2.1± 0.7 *

-2.0± 0.6 **

0

Normal

Female

15

-2.0± 0.6 **

-2.0± 1.0

2.3± 0.9 *

0

Normal

5000

Male

15

-2.1± 1.2

-2.9± 1.1 **

3.3± 1.8 **

0

Normal

Female

15

-1.3± 0.8

-3.6± 0.7 **

2.2± 1.3

1

Normal

Cyclo-phosphamide (60 mg/kg) (positive control)

Male

5

-0.9± 0.4

~± ~

~± ~

0

Normal

Female

5

0.2± 0.3

~± ~

~± ~

0

Normal

 

* p0.05; ** p0.01 by one sided t-test

 

 

 

Summary of micronucleated assay results for XP-2563 PCE ratio and micronucleus data for low dose animals (dosage 500 mg/kg)

Harvest time (hr)

Sex

Number

Mean PCE/ total erythrocyte fraction± sd

Mean micronucleated PCE/1000 PCE± sd

Vehicle control

Test material

Positive control

Vehicle control

Test material

Positive control

24

Male

5

0.54± 0.07

0.48± 0.05

0.50± 0.05

0.2± 0.45

0.2± 0.45

21.2± 18

Female

5

0.55± 0.04

0.53± 0.04

0.52± 0.05

0.4± 0.55

0.6± 0.89

35.6± 12

48

Male

5

0.51± 0.08

0.48± 0.07

~± ~

1.2± 1.79

1.6± 1.34

~± ~

Female

5

0.56± 0.05

0.56± 0.05

~± ~

1.0± 0.71

0.8± 0.84

~± ~

72

Male

5

0.57± 0.08

0.44± 0.07 *

~± ~

1.6± 2.61

1.0± 1.41

~± ~

Female

5

0.60± 0.07

0.57± 0.05

~± ~

1.4± 1.14

0.6± 0.89

~± ~

* p0.05; ** p0.01 by one sided t-test. square root transformed data used for statistical analysis of micronucleated PCE

 

Summary of micronucleated assay results for XP-2563 PCE ratio and micronucleus data for middle dose animals (dosage 2500 mg/kg)

Harvest time (hr)

Sex

Number

Mean PCE/ total erythrocyte fraction± sd

Mean micronucleated PCE/1000 PCE± sd

Vehicle control

Test material

Positive control

Vehicle control

Test material

Positive control

24

Male

5

0.54± 0.07

0.47± 0.06

0.50± 0.05

0.2± 0.45

3.0± 3.54

21.2± 18.0

Female

5

0.55± 0.04

0.55± 0.06

0.52± 0.05

0.4± 0.55

0.6± 0.89

35.6± 12.0

48

Male

5

0.51± 0.08

0.53± 0.09

~± ~

1.2± 1.79

1.2± 0.84

~± ~

Female

5

0.56± 0.05

0.50± 0.07

~± ~

1.0± 0.71

1.0± 0.71

~± ~

72

Male

5

0.57± 0.08

0.57± 0.08

~± ~

1.6± 2.61

0.2± 0.45

~± ~

Female

5

0.60± 0.07

0.51± 0.06 *

~± ~

1.4± 1.14

0.6± 0.89

~± ~

* p0.05; ** p0.01 by one sided t-test. square root transformed data used for statistical analysis of micronucleated PCE

 

Summary of micronucleated assay results for XP-2563 PCE ratio and micronucleus data for high dose animals (dosage 5000 mg/kg)

Harvest time (hr)

Sex

Number

Mean PCE/ total erythrocyte fraction± sd

Mean micronucleated PCE/1000 PCE± sd

Vehicle control

Test material

Positive control

Vehicle control

Test material

Positive control

24

Male

5

0.54± 0.07

0.45± 0.09

0.50± 0.05

0.2± 0.45

0.4± 0.55

21.2± 18.0

Female

5

0.55± 0.04

0.49± 0.04 *

0.52± 0.05

0.4± 0.55

0.6± 0.89

35.6± 17.0

48

Male

5

0.51± 0.08

0.49± 0.04

~± ~

1.2± 1.79

1.0± 1.41

~± ~

Female

5

0.56± 0.05

0.44± 0.03 **

~± ~

1.0± 0.71

0.6± 0.89

~± ~

72

Male

5

0.57± 0.08

0.48± 0.07 *

~± ~

1.6± 2.61

0.4± 0.55

~± ~

Female

5

0.60± 0.07

0.41± 0.06 **

~± ~

1.4± 1.14

1.2± 1.79

~± ~

* p0.05; ** p0.01 by one sided t-test. square root transformed data used for statistical analysis of micronucleated PCE

Applicant's summary and conclusion

Conclusions:
Based on the observations and findings, it is concluded that XP-2563 is not a mammalian genotoxicant in vivo in mouse bone marrow cells under the experimental conditions of the study.
Executive summary:

The potential for XP-2563 to induce chromosomal effects was tested in a mouse bone marrow micronucleus assay. XP-2563 administrated by intraperitoneal injection to groups of male and female CD-1 mice at doses of 500, 2500 or 5000 mg/kg bw. Following the dose, the mouse bone marrow was sampled at 24, 48 and 72 hours. In the micronucleus experiment, one death was observed in the female mice treated with 5000 mg/kg of XP-2563. Indicated by a statistically significant decrease mean body weight and statistically significant decreases in the PCE/total erythrocyte ratio observed in the XP-2563 treated animals. XP-2563 did not induce statistically significant increases in micronucleated PCEs in any of the treated animals. Increases in micronucleated PCE frequency were observed in the positive control group demonstrating the adequacy of the experimental conditions.

Based on the observations and findings, it is concluded that XP-2563 is not a mammalian genotoxicant in vivo in mouse bone marrow cells under the experimental conditions of the study.