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Toxicological information

Repeated dose toxicity: oral

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Administrative data

Endpoint:
short-term repeated dose toxicity: oral
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
other: sufficient documented and scientifically acceptable
Cross-reference
Reason / purpose for cross-reference:
reference to same study

Data source

Reference
Reference Type:
publication
Title:
Toxicity study of a rubber antioxidant, mixture of 2-mercaptomethylbenzimidazoles, by repeated oral administration to rats
Author:
Saitoh M, Umemura T, Kawasaki Y, Momma Y, Matsushima Y, Sakemi K, Isama K, Kitajima S, Ogawa Y, Hasegawa R, Suzuki T, Hayashi M, Inoue T, Ohno Y, Sofuni T, Kurokawa Y, Tsuda M
Year:
1999
Bibliographic source:
Food Chem Toxicol 37, 777-787

Materials and methods

Principles of method if other than guideline:
Male and female rats were treated with MMBIs (2-mercaptomethylbenzimidazoles (a 1:1 mixture of 4-methyl and 5-methyl isomers, MMBIs) by gavage at doses 0 (corn oil), 4, 20 and 100 mg/kg for 28 consecutive days followed by a 2-week recovery period for the control and highest dose groups. Body weight and food consumption, clinical signs, organ weights, clinical biochemistry and hematological parameters including clotting times and micronuclei induction in bone marrow erythropoeitic cells were recorded and a histopathological examination was conducted.
GLP compliance:
not specified

Test material

Constituent 1
Chemical structure
Reference substance name:
1,3-dihydro-4(or 5)-methyl-2H-benzimidazole-2-thione
EC Number:
258-904-8
EC Name:
1,3-dihydro-4(or 5)-methyl-2H-benzimidazole-2-thione
Cas Number:
53988-10-6
Molecular formula:
C8H8N2S
IUPAC Name:
1,3-dihydro-4(or 5)-methyl-2H-benzimidazole-2-thione
Details on test material:
2-Methylmercaptobenzimidazoles (MMBIs, CAS no 53988-10-6, a 1:1 mixture of 2-mercapto-4-methylbenzimidazole, CAS no 27231-33-0 and 2-mercapto-5-methylbenzimidazole, 27231-36-3, mol.wt 164.23 were obtained from Ouchi Shinko Chemical Ind. Ltd (Osaka, Japan)

Test animals

Species:
rat
Strain:
Wistar
Sex:
male/female

Administration / exposure

Route of administration:
oral: gavage
Vehicle:
corn oil
Analytical verification of doses or concentrations:
not specified
Duration of treatment / exposure:
28 days
Frequency of treatment:
daily
Doses / concentrations
Remarks:
Doses / Concentrations:
0, 2, 10, 25, 50, 100, or 150 mg/kg
Basis:
other: nominal
No. of animals per sex per dose:
5 male and 5 female rats/group
Control animals:
yes, concurrent vehicle

Results and discussion

Effect levels

open allclose all
Dose descriptor:
NOAEL
Effect level:
20 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
male
Basis for effect level:
organ weights and organ / body weight ratios
Dose descriptor:
NOAEL
Effect level:
20 mg/kg bw/day (nominal)
Based on:
test mat.
Sex:
female
Basis for effect level:
organ weights and organ / body weight ratios

Target system / organ toxicity

Critical effects observed:
yes
Lowest effective dose / conc.:
100 mg/kg bw/day (nominal)
System:
other: organ weights and organ/body weight ratios of liver and thyroid.
Organ:
kidney
liver
thyroid gland
Treatment related:
yes
Dose response relationship:
yes

Any other information on results incl. tables

In a subacute oral toxicity study with MB2 (2-mercaptomethylbenzimidazole; also named MMBI; 1:1 mixture of 4-ethyl and 5-methyl isomers) male and female rats were treated by gavage at doses of 0 (corn oil), 4, 20 and 100 mg/kg bw/day for 28 consecutive days followed by a 2-week recovery period for the control and highest dose groups. Body weight and food consumption, clinical signs, organ weights, clinical biochemistry and haematological parameters including clotting times, and micronuclei induction in bone marrow erytropoetic cells, and histopathology were examined (Saitoh et al., 1999).

“Relative organ weights of lung, liver and kidney, and serum cholesterol and phospholipid significantly increased in male rats treated with MMBIs at doses of 20 and 100 mg/kg. Males rats administered 100 mg/kg MMBIs exhibited a 1.8 fold increase in thyroid weight associated with histopathological changes but not altered serum thyroid hormone levels. Female rats administered 100 mg MMBIs/kg exhibited significant increases of liver and kidney weights, and serum cholesterol level. No-observed-effect levels for male and female rats were found to be 4 and 20 mg/kg, respectively, in this subacute oral toxicity study”.

Relative lung, liver and kidney weights were significantly increased in male rats treated with 20 mg/kg bw/day. However, absolute lung, liver and kidney weights in male rats were not increased significantly in male rats treated with 20 mg/kg bw/day. The increase in relative organ weights is slight and not evident in the recovery groups at 100 mg/kg bw/day. There is no correlate with histopathology finding in lung, liver and kidneys up to the highest dose of 100 mg/kg bw/day. The effects seen in relative organ weights at 20 mg/kg bw/day are regarded as secondary effects due to the slightly (2.4%) decreased body weight.

Taking the above information into account, the relative organ weight effects at 20 mg/kg bw/day are not considered adverse and the NOAEL for male rats is concluded to be 20 mg/kg bw/day.

In female rats relative and absolute organ weights of lung, liver and kidney were not increased at a dose of 20 mg/kg bw/day.

Therefore, the NOAEL for males and females is 20 mg/kg bw/day.

The PL (phospholipid) level was statistically increased in male rats only at 100 mg/kg bw/day and no effect was observed in female rats at any dose.

A slight but significant higher T-CHO (total cholesterol) level was observed in male rats at doses of 20 mg/kg bw/day and 100 mg/kg bw/day. The increase was approx. 25% and 50 %, respectively. In female rats the T-CHO level was increased at 100 mg/kg bw/day (approx. 25%) only andno significant increase in T-CHO level was observed in female rats at 20 mg/kg bw/day and below.Increased cholesterol levels in this study are accompanied by an increase of liver weights in male and female rats. The increase of cholesterol is interconnected with an increase of the liver weights. The increase of the liver weights is dose dependent and a result of the exposure of the rats to the test substance. Liver weight changes in repeated dose studies in mammalians are often caused by liver enzyme induction. An important function of the liver is to produce and clear cholesterol in the body. If the liver is not working properly, it can cause cholesterol to build up in the body.

In the subacute study by Saitoh et al. (1999), the T-CHO values were only slightly increased in male rats at 20 mg/kg bw/day. The effect was reversible in the recovery group at 100 mg/kg bw/day;  the T-CHO values in the control and the 100 mg/kg bw/day groups were similar and there were no significant differences in liver or thyroid weights in the control and the 100 mg/kg bw/day groups. These data indicate, that the elevated cholesterol levels at 20 mg/kg bw/day are adaptive and should be considered non-adverse.

Applicant's summary and conclusion

Conclusions:
The NOEL (no-observed-effect level) for male and female rats are 4 and 20 mg/kg bw/day, respectively. The NOAEL (no-observed-adverse-effect level) for male and female rats are concluded to be 20 mg/kg bw/day.
Executive summary:

In a subacute oral toxicity study with MB2 (2-mercaptomethylbenzimidazole; also named MMBI; 1:1 mixture of 4-ethyl and 5-methyl isomers) male and female rats were treated by gavage at doses of 0 (corn oil), 4, 20 and 100 mg/kg bw/day for 28 consecutive days followed by a 2-week recovery period for the control and highest dose groups. Body weight and food consumption, clinical signs, organ weights, clinical biochemistry and haematological parameters including clotting times, and micronuclei induction in bone marrow erytropoetic cells, and histopathology were examined (Saitoh et al., 1999).

“Relative organ weights of lung, liver and kidney, and serum cholesterol and phospholipid significantly increased in male rats treated with MMBIs at doses of 20 and 100 mg/kg. Males rats administered 100 mg/kg MMBIs exhibited a 1.8 fold increase in thyroid weight associated with histopathological changes but not altered serum thyroid hormone levels. Female rats administered 100 mg MMBIs/kg exhibited significant increases of liver and kidney weights, and serum cholesterol level. No-observed-effect levels for male and female rats were found to be 4 and 20 mg/kg, respectively, in this subacute oral toxicity study”.

Relative lung, liver and kidney weights were significantly increased in male rats treated with 20 mg/kg bw/day. However, absolute lung, liver and kidney weights in male rats were not increased significantly in male rats treated with 20 mg/kg bw/day. The increase in relative organ weights is slight and not evident in the recovery groups at 100 mg/kg bw/day. There is no correlate with histopathology finding in lung, liver and kidneys up to the highest dose of 100 mg/kg bw/day. The effects seen in relative organ weights at 20 mg/kg bw/day are regarded as secondary effects due to the slightly (2.4%) decreased body weight.

Taking the above information into account, the relative organ weight effects at 20 mg/kg bw/day are not considered adverse and the NOAEL for male rats is concluded to be 20 mg/kg bw/day.

In female rats relative and absolute organ weights of lung, liver and kidney were not increased at a dose of 20 mg/kg bw/day.

Therefore, the NOAEL for males and females is 20 mg/kg bw/day.