Bale Ambuja S, Jackson Meredith D, Krantz Quentin Todd, Benignus Vernon A, Bushnell Philip J, Shafer Timothy J, Boyes William K
Neurotoxicology Division, MD B105-05, National Health and Environmental Effects Research Laboratory, Office of Research and Development, U.S. Environmental Protection Agency, Research Triangle Park, North Carolina 27711, USA.
Toxicol Sci. 2007 Jul;98(1):159-66. doi: 10.1093/toxsci/kfm080. Epub 2007 Apr 9.
Acute exposure to toluene and other volatile organic solvents results in neurotoxicity characterized by nervous system depression, cognitive and motor impairment, and alterations in visual function. In vitro, toluene disrupts the function of N-methyl-D-aspartate (NMDA)-glutamate receptors, indicating that effects on NMDA receptor function may contribute to toluene neurotoxicity. NMDA-glutamate receptors are widely present in the visual system and contribute to pattern-elicited visual-evoked potentials (VEPs) in rodents, a measure that is altered by toluene exposure. The present study tested the hypothesis that effects on NMDA receptors contribute to toluene-induced alterations in pattern-elicited VEPs. Prior to examining the effects of NMDA receptor agonists and antagonists on toluene-exposed animals, a dose-range study was conducted to determine the optimal dose for NMDA (agonist) and MK801 (antagonist). Dose levels of 2.5 mg/kg NMDA and 0.1 mg/kg MK801 were selected from these initial studies. In the second study, Long-Evans rats were exposed to toluene by inhalation, and VEPs were measured during toluene exposure in the presence or absence of NMDA or MK801. Pattern-elicited VEPs were collected by exposing rats to a sinusoidal pattern modulated at a temporal frequency of 4.55 Hz. Following collection of baseline VEPs, rats were injected with either saline, NMDA (2.5 mg/kg, ip), or MK801 (0.1 mg/kg, ip) and 10 min later were exposed to air or toluene (2000 ppm). VEP amplitudes were calculated for 1x (F1) and 2x stimulus frequency (F2). The F2 amplitude was reduced by approximately 60, 60, and 50% in the toluene-exposed groups (TOL): SALINE/TOL (n = 11), NMDA/TOL (2.5 mg/kg; n = 13), and NMDA/TOL (10 mg/kg, n = 11), respectively. Thus, NMDA (2.5 and 10 mg/kg) did not significantly affect toluene-mediated F2 amplitude effects. Administration of 0.1 mg/kg MK801 prior to toluene exposure blocked the F2 amplitude decreases caused by toluene (n = 9). However, when 0.1 mg/kg MK801 was administered 20 min after the onset of toluene exposure, toluene-mediated F2 amplitude decreases persisted despite the challenge by MK801. These data support the hypothesis that acute actions of toluene on pattern-elicited VEPs involve NMDA receptors.
急性接触甲苯和其他挥发性有机溶剂会导致神经毒性,其特征为神经系统抑制、认知和运动功能受损以及视觉功能改变。在体外,甲苯会破坏N-甲基-D-天冬氨酸(NMDA)-谷氨酸受体的功能,这表明对NMDA受体功能的影响可能是甲苯神经毒性的原因之一。NMDA-谷氨酸受体广泛存在于视觉系统中,并有助于啮齿动物的模式诱发视觉诱发电位(VEP),这一指标会因接触甲苯而改变。本研究检验了以下假设:对NMDA受体的影响是甲苯诱导的模式诱发VEP改变的原因。在研究NMDA受体激动剂和拮抗剂对甲苯暴露动物的影响之前,进行了一项剂量范围研究,以确定NMDA(激动剂)和MK801(拮抗剂)的最佳剂量。从这些初步研究中选择了2.5 mg/kg NMDA和0.1 mg/kg MK801的剂量水平。在第二项研究中,Long-Evans大鼠通过吸入接触甲苯,并在接触甲苯期间,在有或没有NMDA或MK801的情况下测量VEP。通过将大鼠暴露于以4.55 Hz时间频率调制的正弦模式来收集模式诱发的VEP。在收集基线VEP后,给大鼠注射生理盐水、NMDA(2.5 mg/kg,腹腔注射)或MK801(0.1 mg/kg,腹腔注射),10分钟后将其暴露于空气或甲苯(2000 ppm)中。计算1倍(F1)和2倍刺激频率(F2)下的VEP振幅。在甲苯暴露组(TOL)中,F2振幅分别降低了约60%、60%和50%:生理盐水/甲苯组(n = 11)、NMDA/甲苯组(2.5 mg/kg;n = 13)和NMDA/甲苯组(10 mg/kg,n = 11)。因此,NMDA(2.5和10 mg/kg)对甲苯介导的F2振幅影响没有显著作用。在甲苯暴露前给予0.1 mg/kg MK801可阻断甲苯引起的F2振幅降低(n = 9)。然而,当在甲苯暴露开始后20分钟给予0.1 mg/kg MK801时,尽管受到MK801的挑战,甲苯介导的F2振幅降低仍然存在。这些数据支持了以下假设:甲苯对模式诱发VEP的急性作用涉及NMDA受体。