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. 2015 Nov 4;149(2):335–345. doi: 10.1093/toxsci/kfv237

FIG. 3.

FIG. 3.

Latency to wild running (WR) (A) and clonus (CL) (B) in females. Latency to WR (C) and CL (D) in males. n = 9 for controls and 8 for PCB-exposed group for both males and females. * indicates that the 6 mg/kg PCB exposure group significantly differed from the control group (P < .001).