PubMed Health⌕ Search

Biomedical subjects

D W Herr

Publications and source records attributed to D W Herr.

At least 19 recordsLinked to original sources

A system for simultaneous multiple subject, multiple stimulus modality, and multiple channel collection and analysis of sensory evoked potentials.

A system has been developed for collecting sensory evoked potentials simultaneously from multiple channels for multiple subjects at up to 80 kHz sample rate per channel. Sample rates up to 200 kHz are available for four or less chambers and a single channel per chamber. A variety of visual, somatosensory, and auditory stimuli may be presented singly or simultaneously. Collected waveforms are associated with searchable text (metadata) to allow convenient selection from a relational database. Multiple waveforms can then be easily grouped for analysis and processed. Results can be exported to other software for further graphics or statistical processing. Scripting and event logging are available to provide automation and improve data confidence. Sample data are presented from control animals for each of the sensory modalities for comparison with historical data collected from other systems.

Animals↗

Repeated exposure of adult rats to Aroclor 1254 causes brain region-specific changes in intracellular Ca2+ buffering and protein kinase C activity in the absence of changes in tyrosine hydroxylase.

Polychlorinated biphenyls (PCBs) are ubiquitous environmental contaminants, some of which may be neurotoxic. In vitro studies from this laboratory indicated that noncoplanar PCBs perturbed intracellular signal transduction mechanisms including Ca2+ homeostasis, receptor-mediated inositol phosphate production, and translocation of protein kinase C (PKC). In the present study, we examined the effects of PCBs in vivo by dosing adult male Long-Evans rats orally with Aroclor 1254 (0, 10, or 30 mg/kg/day; 5 days/week for 4 weeks) in corn oil. At 24 h after the last dose, rats were tested for motor activity in a photocell device for 30 min. Immediately, the rats were euthanized, blood was collected for thyroid hormone analysis, and brains were removed, dissected into regions (cerebellum, frontal cortex, and striatum), and subcellular fractions were obtained for neurochemical analysis. Following Aroclor 1254 treatment, body weight gain in the high-dose group was significantly lower than the control and low-dose groups. Horizontal motor activity was significantly lower in rats dosed with 30 mg/kg Aroclor 1254. Ca2+ buffering by microsomes was significantly lower in all three brain regions from the 30 mg/kg group. In the same dose group, mitochondrial Ca2+ buffering was affected in cerebellum but not in cortex or striatum. Similarly, total cerebellar PKC activity was decreased significantly while membrane-bound PKC activity was significantly elevated at 10 and 30 mg/kg. PKC activity was not altered either in cortex or the striatum. Neurotransmitter levels in striatum or cortex were slightly altered in PCB-exposed rats compared to controls. Furthermore, repeated oral administration of Aroclor 1254 to rats did not significantly alter forebrain tyrosine hydroxylase immunoreactivity or enzymatic activity. Circulating T4 (total and free) concentrations were severely depressed at both doses in Aroclor 1254-exposed rats compared to control rats, suggesting a severe hypothyroid state. These results indicate that (1) in vivo exposure to a PCB mixture can produce changes in second messenger systems that are similar to those observed after in vitro exposure of neuronal cell cultures; (2) second messenger systems seem to be more sensitive than alterations in neurotransmitter levels or tyrosine hydroxylase involved in dopamine synthesis during repeated exposure to PCBs; and (3) the observed motor activity changes were independent of changes in striatal dopamine levels.

Animals↗

Trichloroethylene ototoxicity: evidence for a cochlear origin.

Trichloroethylene (TCE) is known to produce an unusual pattern of hearing impairment in laboratory animals marked by a preferential loss of threshold sensitivity at midfrequencies. The purpose of this research was to determine whether the TCE-induced auditory deficit results from cochlear dysfunction. Adult Long Evans hooded rats were exposed via inhalation to either 0 (clean air) or 4000 ppm TCE (6 h/day for 5 days). Auditory thresholds for 1-40 kHz tones were determined 3 weeks after exposure using reflex modification audiometry (RMA; n = 12/group). Cochlear electropotentials were measured during subsequent testing (n = 3-10/group) 5 to 7 weeks after exposure, including thresholds for cochlear action potentials (CAP) and the 1-microV cochlear microphonic for 2-40 kHz tones, and the N1 amplitude intensity function (40-90 dB SPL). Cochlear histopathology was assessed in midmodiolar preparations of a separate set of animals, exposed as before (n = 4/group). RMA testing confirmed a TCE-induced loss in midfrequency threshold sensitivity (8 and 16 kHz). CAP thresholds were elevated at midfrequencies (8 and 16 kHz) among TCE-treated subjects, along with a suppression of the N1 amplitude from 50 to 90 dB SPL. The cochlear microphonic, a nonpropagated ac potential generated largely by the outer hair cells, was not affected by the TCE treatment. Cochlear histopathology revealed a loss of spiral ganglion cells that was significant in the middle turn, but not in the basal turn. There was an inconsistent loss of hair cells among treated subjects. The data suggest strongly that the behaviorally determined loss in auditory function can be accounted for by a cochlear impairment and that the spiral ganglion cell may be a prominent target of TCE.

Animals↗

Carbon disulfide neurotoxicity in rats: VI. Electrophysiological examination of caudal tail nerve compound action potentials and nerve conduction velocity.

The effects of subchronic exposure to carbon disulfide (CS2) on ventral caudal tail nerve compound nerve action potential (CNAP) amplitudes and latencies, and nerve conduction velocity (NCV) in rats were examined. Male and female Fischer 344 rats were exposed to 0, 50, 500, or 800 ppm CS2 for 6 hrs/day, 5 days/week. Using separate groups, exposure duration was 2, 4, 8, or 13 weeks. Exposure to 500 or 800 ppm CS2 for 13 weeks decreased NCV compared to the 50 ppm CS2 group. CNAP amplitudes were increased, and peak P1P2 interpeak latency decreased, after exposure to 500 or 800 ppm CS2 for 13 weeks. Most of the changes in NCV and CNAPs were not attributable to differences in tail or colonic temperature. However, the increases in peak P1 amplitude may relate to the proximity of the electrodes to the tail nerves. Assessment of tail nerve morphology after 13 weeks exposure to 800 ppm CS2 revealed only minor changes compared to the extent of axonal swelling and degeneration observed in the muscular branch of the tibial nerve and axonal swelling in the spinal cord. As anticipated, in older animals the NCV increased, the CNAP amplitudes increased, and the CNAP latencies decreased. The biological basis for the changes in CNAPs produced by CS2 is under investigation. Future studies will focus on electrophysiological evaluation of spinal nerve function, to allow better correlation with pathological and behavioral endpoints.

Action Potentials↗

A comparison of the acute neuroactive effects of dichloromethane, 1,3-dichloropropane, and 1,2-dichlorobenzene on rat flash evoked potentials (FEPs).

Previous research showed that acute exposure to dichloromethane (DCM) produced a selective reduction in peak N30 of flash evoked potentials (FEPs) in rats. In contrast, acute exposures to p-xylene or toluene selectively reduced FEP peak N160. The present experiments compared the effects of DCM (log P = 1.25; oil:water partition coefficient), 1,3-dichloropropane (DCP; log P = 2.00), and 1,2-dichlorobenzene (DCB; log P = 3.38) on FEPs recorded from adult Long-Evans rats. Before administration of test compounds, FEPs were recorded for five daily sessions to develop FEP peak N160. Test compounds were dissolved in corn oil and administered i.p. at doses based on proportions of their LD50 values. The doses were: DCM, 0, 57.5, 115, 230, or 460 mg/kg; DCP, 0, 86, 172, 343, or 686 mg/kg; and DCB, 0, 53, 105, 210, or 420 mg/kg. Testing times after dosing varied among compounds and were based on pilot studies to measure both the times of peak effect and recovery. Each solvent produced significant changes in the latency and amplitude of multiple components of the FEP waveforms. However, the predominant effect of DCM was to reduce the amplitude of peak N30 (ED50 = 326.3 mg/kg), that of DCP was to reduce both peaks N30 (ED50 = 231.0 mg/kg) and N160 (ED50 = 136.8 mg/kg), and that of DCB was to reduce peak N160 (ED50 = 151.6 mg/kg). There was no consistent relationship between log P values and the potency of the compounds to alter FEP peaks N30 and N160. The results suggest that organic solvents have multiple acute effects on the function of the central nervous system, which are not predictable solely by the compound's lipid solubility.

Animals↗

Developmental exposure to Aroclor 1254 produces low-frequency alterations in adult rat brainstem auditory evoked responses.

Developmental exposure of Long-Evans rats to 0, 1, 4, or 8 mg/kg/day Aroclor 1254 (A1254) from Gestational Day 6 through Postnatal Day 21 produces an elevated behavioral threshold for a 1-kHz tone. Brainstem auditory evoked responses (BAERs) were assessed in a subset of these animals (about 1 year old) using filtered clicks at 1 (65 and 80 dB SPL), 4 (60 and 80 dB SPL), 16 (40 and 80 dB SPL), and 32 (40 and 80 dB SPL) kHz. Aroclor 1254 decreased BAER amplitudes at 1 and 4 kHz, but not at 16 or 32 kHz. A dose-related decrease in the baseline-to-peak P1A amplitude was observed for the 1-kHz (80-dB) stimulus. Doses of 1, 4, or 8 mg/kg/day A1254 decreased the peak-to-peak amplitude of both P1AN1 and P1BN1 for a 1-kHz (80-dB) stimulus. Doses of 4 and 8 mg/kg/day A1254 decreased the peak-to-peak amplitude of N1P2 and P2N2 for a 4-kHz (60-dB) or 1-kHz (80-dB) stimulus. At 8 mg/kg/day, A1254 also increased the latency of peak P4 at 1 kHz (65 dB). The decreases in peak P1A amplitudes are consistent with a dysfunction of the cochlea and/or auditory nerve. Together, the data confirm that developmental exposure of rats to A1254 produces a permanent low- to mid-frequency auditory dysfunction and suggest a cochlear and/or auditory nerve site of action.

Animals↗

Possible confounding effects of strobe "clicks" on flash evoked potentials in rats.

Flash evoked potentials (FEPs) undergo within- and between-session changes and are modified by auditory white noise (26). We examined whether an auditory potential produced by the "click" associated with the strobe discharge could be recorded, and if alterations in an auditory response could explain the within- and between-session changes in FEPs. We also examined differences between a frontal cortex or a nasal reference electrode location on FEPs and auditory potentials. An auditory potential associated with the strobe discharge could be clearly recorded. This response was eliminated by the presence of 80 dB SPL masking white noise. However, the within- and between-session changes in FEPs could not be explained by modifications of the auditory potential. Animals whose ear drums were ruptured did not exhibit an auditory response, and their FEPs were similar to those of controls tested in the presence of masking white noise. A nasal reference electrode decreased the impact of auditory potentials on FEPs, but allow visual potentials (electroretinogram and optic tract activity) to influence FEPs. The data show that auditory potentials associated with the strobe discharge can be recorded from the visual cortex of rats, and that these auditory responses represent a possible confounding factor in the interpretation of toxicological studies employing FEPs.

Acoustic Stimulation↗

Effects of 3,3'-iminodipropionitrile on the peripheral structures of the rat visual system.

Adult male Long-Evans rats received 3,3'-iminodipropionitrile (IDPN; 400 mg/kg i.p.) and were killed one day after one dose, or one, three, seven, thirty-five, or seventy day(s) following 3 consecutive daily doses for histological analysis of the eye. Histological alterations in visual structures were not observed before one day after the third dose of IDPN. Somato-dendritic swelling of cells in the inner nuclear (IN) layer was seen prior to retinal detachment (1 day after cessation of dosing) followed by progressive retinal degeneration (35 and 70 days). IDPN exposure resulted in opacification of the cornea and vascular hemorrhaging into the subretinal space (3 days) followed by complete detachment of the retina (7 days). The corneal opacification was transient and resolved by 14 days post-treatment. The retina underwent complete spontaneous reattachment between 35 and 70 days after IDPN administration. A subsequent experiment was performed to characterize the dose-response of IDPN on retinal histology, 2 weeks after the last dose (0, 100, 200, 400 mg/kg x 3 days). In the dose-response experiment, retinal detachment and degeneration in the IN layer were only apparent in the 400 mg/kg dose group. However, increased GFAP immunoreactivity in the retina was observed in the 200 mg/kg dose group without overt retinal pathology. Results indicate that the corneal opacification, vascular hemorrhaging, and detached retinae recovered in a time-dependant manner, while neurodegeneration of the visual retina was progressive, even after the retina had reattached. The present study indicates that this toxicant may have direct effects on both neural and non-neural structures, and characterizes the time-course and dose-response of histopathological changes in the retina.

Animals↗

Comparison of intracranial infusions of colchicine and ibotenic acid as models of neurodegeneration in the basal forebrain.

Colchicine and ibotenic acid were compared for their ability to produce neurodegeneration and cognitive deficit after bilateral infusions into the nucleus basalis magnocellularis of male Long-Evans rats. Four weeks post-lesion, there was no difference in locomotor activity following infusion of either neurotoxicant or vehicle. In a passive avoidance task, both treated groups had significantly shorter step-through latencies compared with vehicle. Five weeks post-lesion, rats were killed for neurochemistry or histochemistry. Choline acetyltransferase (ChAT) activity in both the frontal and parietal cortex was significantly decreased (25-35%) in the colchicine- and ibotenic acid-infused rats when compared to control. There was no effect of either neurotoxicant on ChAT activity in the hippocampus or striatum. Both neurotoxicants produced damage in the general area of the ventromedial pallidum, although ibotenic acid infusion consistently produced a larger area of damage as assessed in Nissl-stained sections. Analysis of the number of ChAT-immunoreactive cells in the nucleus basalis magnocellularis (NBM) showed an average 60% cell loss following colchicine infusion and a 75% cell loss after ibotenic acid infusion. Area of glutamic acid decarboxylase (GAD) staining was significantly decreased in several regions surrounding the NBM for ibotenic acid (51% average decrease), and showed non-significant decreases (28%) following colchicine infusion. Colchicine infusion decreased dopamine and 3,4-dihydroxyphenylacetic acid (DOPAC) in the striatum; ibotenic acid had no effect on brain catechol of indoleamine levels. The results indicate that although similar cholinergic hypofunction and behavioral deficits were achieved, several non-cholinergic differences between the neurotoxicants were detected.

Animals↗

Within-session changes in peak N160 amplitude of flash evoked potentials in rats.

The negative peak occurring approximately 160 ms after stimulation (peak N160) of flash evoked potentials (FEPs) of rats changes with repeated testing. Habituation, sensitization, and arousal have all been invoked to explain these changes, but few studies have directly tested these explanations. We examined within-session changes in peak N160 amplitude with repeated testing, and the modulatory effects of stimulus intensity and auditory white noise. Peak N160 amplitude increased with daily testing (between-session changes), and was larger at greater stimulus intensities. In contrast, peak N160 amplitude underwent within-session increases on early days and within-session decreases on later days. The within-session changes were not affected by stimulus intensity. In rats previously tested in a quiet environment, exposure to acoustic white noise increased motor activity and transiently decreased peak N160 amplitude, which then increased and subsequently decreased with continued photic and acoustic stimulation. Repeated testing in the presence of noise did not alter the within-session changes in peak N160 amplitude. Heart rate showed both within- and between-session decreases, but was unaffected by noise. The data suggest that the within-session changes in peak N160 amplitude may reflect a habituation-like response to the test environment.

Acoustic Stimulation↗

Alterations in rat flash and pattern reversal evoked potentials after acute or repeated administration of carbon disulfide (CS2).

Because solvents may selectively alter portions of visual evoked potentials, we examined the effects of carbon disulfide (CS2) on flash (FEPs) and pattern reversal (PREPs) evoked potentials. Long-Evans rats were administered ip carbon disulfide either acutely or for 30 days. FEPs or PREPs were recorded prior to and 1, 2, 4, 8, or 24 hr after a single dose of CS2 (0, 100, 200, 400, or 500 mg/kg). Flash evoked potentials were also recorded 1, 2, 6, and 24 hr after the last of 30 doses of 200 mg CS2/kg/day. Acute exposure to CS2 consistently decreased the amplitude of FEP peak N160 at 1 hr, depressed peak N30 amplitude over 2-4 hr, and increased the latency of peaks P21, N30, P46, N56, and N160 for up to 4 hr after treatment. Carbon disulfide decreased the amplitude of PREP peaks P65, N83, P88, and N122 4 hr after treatment. Colonic temperature was depressed up to 8 hr after treatment. Administration of 200 mg CS2/kg/day decreased the amplitude of FEP peak N30 and increased the latencies of peaks P21, N30, P46, N56, and N160 up to 24 hr after the last dose. The differential effects of CS2 on portions of FEPs indicate that FEP peaks can be independently modulated. Changes in PREPs were temporally correlated with alterations in early FEP peaks, but FEP peak N160 was depressed at an earlier time point. Repeated CS2 exposure affected FEPs at lower doses and for a longer time than an acute exposure, similar to the reported greater severity of neurological disturbances following repeated CS2 exposures in humans.

Animals↗

Rat flash-evoked potential peak N160 amplitude: modulation by relative flash intensity.

The flash-evoked potential (FEP) of rats has a large negative peak (N160) approximately 160 ms following stimulation. This peak has been reported to be modulated by the subject's state of behavioral arousal and influenced by several test parameters. These experiments examined the influences of repeated testing, the number of stimuli/session, interactions of ambient illumination and flash intensity, and the effect of pupillary dilation on the development and amplitude of peak N160. The amplitude of peak N160 increased with daily testing and reached an asymptotic amplitude by about day 10. This amplitude was affected by the intensity of the flash stimulus relative to the ambient illumination (RFI) and appeared to reach a "ceiling" amplitude at greater than 50 dB RFI. The number of stimuli/session and dilation of the subject's pupils did not have a large influence on the growth or asymptotic level of peak N160 amplitude. The data are consistent with the hypothesis that the growth of peak N160 may represent a sensitization-like phenomenon.

Animals↗

Subchronic toxicity studies indicate that tris(2-chloroethyl)phosphate administration results in lesions in the rat hippocampus.

Tris(2-chloroethyl)phosphate (TRCP), a flame-retardant plasticizer used in plastics, polymeric foams and synthetic fibers, was studied as part of the National Toxicology Program's class study of phosphate flame-retardants. TRCP was administered at 0, 22, 44, 88, 175 and 350 mg/kg to both sexes of rats and 0, 44, 88, 175, 350 and 700 mg/kg to both sexes of mice in both fourteen day repeat dose and sixteen week subchronic studies. Results of these studies showed that TRCP toxicity in the 14-day studies was limited to modest increases in male rat kidney and female rat liver weights. Little evidence of toxicity was observed in mice in the 14 day studies. Toxicity observed in mice in the sixteen week studies was limited to increased liver weights in both sexes and decreased kidney weights in males. Administration of TRCP to rats for sixteen weeks resulted in increased mortality of both males and females, increased liver and kidney weights and a lesion in the hippocampal region of the brain. The lesion observed in rat brain appeared as loss of the pyramidal neurons of the CA1 region of the hippocampus and was both more common and more severe in female rats. This lesion, which was not observed in mice, is unusual for any chemical and is unique for a trialkyl phosphate such as TRCP. It is speculated that this highly directed toxicity of TRCP might be used as a chemical probe to investigate the role of the hippocampus in behavior and other functions.

Animals↗

Blockade of only spinal alpha 1 adrenoceptors is insufficient to attenuate DDT-induced alterations in motor function.

Male Fischer 344N rats were chronically implanted with an intrathecal cannula and gavaged with p,p'-DDT (1,1,1-trichloro-2,2-bis[p-chlorophenyl]ethane; 30 or 45 mg/kg) or corn oil. Seven hours later, subjects were intrathecally infused with vehicle, 15, 30, 60, or 120 micrograms of prazosin (an alpha 1-adrenergic antagonist). Spectral analysis of bodily movements was performed 7.5, 8, and 10 hr after DDT administration. In control rats, 15 micrograms of prazosin reduced the spectral profiles of spontaneous movements. A 30-micrograms dose produced motor impairments, without significantly changing the spectral profiles. Tremulous movements induced by DDT were unaffected by 15 or 30 micrograms, whereas 60 or 120 micrograms of intrathecal prazosin significantly reduced the spectral profiles of rats pretreated with 45 mg/kg of DDT. Other subjects were administered vehicle or DDT (45 mg/kg), intrathecally infused with 15 or 60 micrograms of prazosin (7 hr), and sacrificed (7.5 hr). Noncannulated rats were gavaged with 60 mg/kg of DDT, injected subcutaneously (sc) with 0.5 mg/kg of prazosin (5.5 hr), and sacrificed (8 hr). Cortical and spinal tissues were used in ex vivo binding assay utilizing [3H]prazosin. Fifteen or sixty micrograms of intrathecal prazosin occupied similar percentages of spinal [3H]prazosin binding sites, but produced a dose-related increase in cortical prazosin equivalents. Sixty micrograms of intrathecal or 0.5 mg/kg of sc prazosin resulted in similar concentrations of cortical prazosin equivalents. Together, these data indicate that while intrathecal prazosin will attenuate DDT-induced motor dysfunction, this effect requires blockade of alpha 1 adrenoceptors in regions other than solely the spinal cord.

Analysis of Variance↗

Buffer effects on high affinity [3H]-prazosin binding in brain and spinal cord.

[3H]-Prazosin binding was characterized in cortical and spinal membranes from Fischer 344N and Sprague-Dawley rats. Estimates of Bmax and Kd values were comparable with earlier studies of these regions in the central nervous system (CNS). However, the Kd obtained using Tris buffer system was greater than when HEPES or phosphate buffer was used. These data indicate that high affinity [3H]-prazosin binding in the homogenates of tissue from the CNS is affected critically by buffer selection.

Animals↗

Pharmacological modification of tremor and enhanced acoustic startle by chlordecone and p,p'-DDT.

Pretreatment of rats with phenoxybenzamine (5 mg/kg; SC), an alpha adrenergic antagonist, decreased the peak tremor power and startle magnitude of rats subsequently given DDT (75 mg/kg; PO) or chlordecone (60 mg/kg; IP), without having a significant effect on control animals. Pretreatment with an intracerebroventricular injection of calcium (3.75 microM in 5 microliters NaCl) decreased the peak tremor power due to subsequently administered DDT, while increasing the tremor response in rats later dosed with chlordecone. The effects of phenoxybenzamine are postulated to be due to a blockade of an excitatory influence of the adrenergic system. Calcium may decrease DDT-induced tremor by acting as a neuronal stabilizer. Potentiation of the tremorigenic effect of chlordecone by calcium may be due to increased levels of intracellular calcium, resulting in augmented release of neurotransmitters in chlordecone-exposed animals.

Acoustic Stimulation↗

Modulation of p,p'-DDT-induced tremor by catecholaminergic agents.

p,p'-DDT (1,1,1-trichloro-2,2-bis(p-chlorophenyl)ethane; 75 mg/kg) or corn oil was administered po to male Fischer 344N rats. Tremor was quantified 8 hr later by spectral analysis of whole body movements. The effect of sc injection of pharmacological challenges on the spectral profile of body movements was determined. The alpha antagonist phenoxybenzamine decreased the intensity of movements over most of the power spectra in animals exposed to DDT, but decreased spectral power only at lower frequencies in control subjects. The alpha-1 antagonist prazosin had similar effects in animals given DDT. The alpha-2 antagonist yohimbine and the beta antagonist propranolol produced lethality and increased the intensity of movements in animals administered DDT, without significantly affecting control animals. The alpha-2 agonist clonidine decreased the spectral profile over a wide range of frequencies in animals exposed to DDT, while depressing the spectral power of control animals only at higher frequencies. The dopamine antagonist haloperidol increased the intensity of movements in DDT-treated animals, without altering the spectral profile of controls. The dopamine agonist apomorphine induced stereotypy in control animals, but failed to significantly alter the power spectra in subjects given DDT. These data suggest a facilitatory and inhibitory role, respectively, for alpha-1 and alpha-2 receptors in the modulation of DDT-induced tremor. Dopamine and beta receptors may be involved in the tonic inhibition of tremor produced by DDT.

Animals↗

Neurochemical effects of DDT in rat brain in vivo.

p,p'-DDT and related agents act to hold the sodium channel open once opened and this effect is believed to be responsible for neurological effects of tremor and hyperexcitability in vivo. There is a good correlation between DDT-induced tremor and an increase in the levels of the metabolites of norepinephrine (NE), serotonin (5HT) and, to a lesser extent, dopamine (DA) in the brain stem (BS), hypothalamus (HYP), striatum (STR), or hippocampus (HPC). DDT also increases levels of excitatory amino acids glutamate (GLU) and aspartate (ASP), but the effect occurs only in the brain stem. These effects are dose- and time-related. Pharmacological studies found that blockade of alpha 1-adrenergic receptors attenuate DDT-induced tremor, while blockade of serotonergic, cholinergic muscarinic, and dopaminergic receptors augment the toxicity of DDT. Tremor was almost completely blocked in rats pretreated with hydantoin, an anticonvulsant believed to block repetitive firing of nerves by interfering with the inactivation gate of the sodium channel. A similar antagonism was observed for permethrin, a Type I pyrethroid believed to have a mechanism of action very similar to that of DDT. However, hydantoin increased the tremorigenic effects of chlordecone, an organochlorine whose mechanism has not been linked to the sodium channel. These data are consistent with the hypothesis that the in vivo neurotoxicity of some organochlorine insecticides is related to their effects on the sodium channel.

Amino Acids↗