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. Author manuscript; available in PMC: 2016 Dec 1.
Published in final edited form as: Food Chem Toxicol. 2015 Sep 30;86:104–115. doi: 10.1016/j.fct.2015.09.017

Table 4.

Incidence of non-neoplastic lesions in male and female F344/N rats administered 0, 0.0875, 0.175, 0.35, or 0.70 mM glycidamide in the drinking water for two yearsa.

Non-neoplastic lesion Sex Glycidamide (mM)
0 0.0875 0.175 0.35 0.70
Brain gliosis Male 0/48 (0%)** 1/48 (2%) 0/48 (0%) 0/47 (0%) 4/48 (8%)*
Female 0/48 (0%)** 0/48 (0%) 4/48 (8%)* 4/48 (8%)* 4/48 (8%)*
Liver hepatocyte
degeneration
Male 2/47 (4%)** 6/47 (13%) 6/48 (13%) 10/47 (21%)** 8/47 (17%)**
Liver necrosis Male 1/47 (2%)* 5/47 (11%) 2/48 (4%) 7/47 (15%)* 5/47 (11%)*
Spinal cord (lumbar)
axonal degeneration
Female 5/48 (10%)* 6/48 (13%) 5/47 (11%) 6/48 (13%) 9/48 (19%)*
Uterus endometrium
cystic hyperplasia
Female 11/48 (23%)*** 17/48 (35%) 14/48 (29%) 14/48 (29%) 23/48 (48%)***
a

The data are reported as the number of animals with a non-neoplastic lesion per number of animals examined microscopically and (in parentheses) the % incidence. Statistical analyses for dose-related trends and differences in incidence were conducted by survival-adjusted Poly-3 tests.

An asterisk (*) associated with the 0 mM glycidamide incidence indicates a significant (*, p ≤ 0.05; **, p ≤ 0.01; ***, p ≤ 0.001) dose-related trend with respect to glycidamide. An asterisk (*) associated with a specific treatment indicates a significant (*, p ≤ 0.05; **, p ≤ 0.01; ***, p ≤ 0.001) difference compared to the 0 mM glycidamide incidence.