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Biomedical subjects

K M Crofton

Publications and source records attributed to K M Crofton.

At least 73 records · Page 4Linked to original sources
PubMed1984

Effects of two pyrethroid insecticides on motor activity and the acoustic startle response in the rat.

To better characterize the behavioral toxicity of pyrethroid insecticides, comparisons were made of the effects of cismethrin and deltamethrin exposure on motor activity and the acoustic startle response in male Long-Evans rats. Acute dose-effect, acute time course, and 30-day repeated-exposure determinations of 1-hr motor activity were made using figure-eight mazes. The acoustic startle response was measured to a 13-kHz, 120-dB(A), 40-msec tone at each of three background white noise levels (50, 65, and 80 dB). Deltamethrin (0, 2, 6, or 8 mg/kg) or cismethrin (0, 6, 12, 18, or 24 mg/kg) were administered po in 0.2 ml/kg corn oil. Cismethrin and deltamethrin produced similar dosage-dependent decreases in motor activity. The time course of onset and recovery for this decreased activity was rapid (1 to 4 hr) No cumulative effects on motor activity of a 30-day exposure to 2 mg/kg/day deltamethrin or 6 mg/kg/day cismethrin were found. The effects of cismethrin and deltamethrin on the acoustic startle response were dissimilar: deltamethrin produced a dosage-dependent decrease in amplitude and an increase in latency, and cismethrin produced an increase in amplitude and no change in latency. The differential effects of cismethrin and deltamethrin on the acoustic startle response may be related to the contrasting effects previously shown with neurophysiological and/or neurochemical techniques.

Administration, Oral↗
PubMed1984

Thioridazine and the neuroleptic radioreceptor assay.

When the neuroleptic radioreceptor assay (NRRA) has been used to monitor total neuroleptic-like activity (NLA) in the blood of patients taking thioridazine, the NLA values obtained from the NRRA are much lower than values calculated in the same sample by measuring the actual concentrations of parent drug and active metabolites and multiplying these values by the relative potency of each compound. The present report demonstrates that in the NRRA for thioridazine or its active metabolites, the normal displacement of [3H]-spiperone from striatal membranes by thioridazine is altered in the presence of sera. The inclusion of serum (50 microliter/ml) distorts the sigmoidal displacement curves, such the resulting log-logit (or Hill) slope is markedly decreased. Similar serum-induced changes in the log-logit slope are seen for two active metabolites of thioridazine, but not for chlorpromazine or haloperidol. As a consequence, when one of these latter drugs is used as a standard, the NRRA substantially underestimates the actual NLA (chlorpromazine equivalents) values for patients treated with thioridazine. Moreover, because of differences in the magnitude of the effect with serum from different individuals, it is not possible to control completely for this effect. Thus, these data reconcile discrepancies that have been reported for data from the NRRA versus that from direct analytical measurements, and demonstrate that the use of the NRRA as a quantitative tool in the clinical pharmacology of thioridazine may lead to erroneous estimations of active drug and metabolites in the blood.

Animals↗
PubMed1983

Use of environmental challenges in behavioral toxicology.

The term environmental challenges encompasses variables that are either known or suspected to affect a baseline of behavior. Environmental challenges can be used to provide information that is important for characterizing the behavioral effects of prior exposure to a toxicant, as well as for revealing effects of the toxicant that may not otherwise be apparent in the baseline under investigation. The use of environmental challenges can be applied in studies of all known classes of behavior, and in each case is limited only to the extent that appropriate variables can be identified and manipulated. Use of environmental challenges may be particularly relevant for studies of schedule-controlled operant behavior because many of the controlling variables have already been well specified. The rationale for using environmental challenges to characterize the behavioral effects of toxicants is very similar to that for using pharmacological challenges; both represent promising new research strategies in behavioral toxicology.

Animals↗
PubMedDate not supplied

Pyrethroid effects on schedule-controlled behavior: time and dosage relationships.

Pyrethroid insecticides have been divided into Types I and II based on behavioral profiles of toxicity produced by life-threatening dosages. In order to assess potential alterations in acquired (operant) behavior, acute dosage-effect and time-course determinations for permethrin (Type I) and cypermethrin (Type II) were made. Long-Evans rats responded for food according to a multiple schedule consisting of four different variable-interval schedules. Permethrin (100-400 mg/kg) and cypermethrin (7.5-60 mg/kg) were administered PO 1.5 hr pre-session and their effects on response rates and between-component response patterning determined. Permethrin reduced responding in a manner which was independent of the baseline response rate, while the rate reductions following cypermethrin administration showed a dependence on the baseline levels of responding, with low response rates showing differential sensitivity to disruption. When select dosages of each compound were delivered at various pre-session times, onset of and recovery from the rate-decreasing effects were more rapid with cypermethrin, with rates returning to baseline levels by 12 hr post-dosing. Responding was maximally suppressed 24 hr after administration of permethrin and returned to baseline levels 48 hr after administration. The disruption of response patterning following cypermethrin was maximal at 1.5 hr after administration, with complete recovery 12 hr post-dosing. Differential effects on response patterning, in potency, and in the time-course of effects of permethrin and cypermethrin suggest a type-specificity for pyrethroid effects on schedule-controlled behavior at dosages far below those producing lethality in rats.

Animals↗
PubMedDate not supplied

Reflex modification and the detection of toxicant-induced auditory dysfunction.

There are numerous environmental chemicals that adversely impact sensory functioning in exposed populations. Test methods are needed that can rapidly and efficiently assess the potential of chemicals to induce sensory toxicity. Reflex modification of the startle response is a technique that provides rapid, objective and quantitative assessments of sensorimotor function. This procedure has been shown to be sensitive to a variety of neurotoxic compounds. Reflex modification can also provide independent estimates of chemical-induced alterations in both sensory and motor function. Future efforts should focus on expanding the use of this procedure in both the identification and characterization of neurotoxic chemicals.

Animals↗
PubMedDate not supplied

Auditory deficits and motor dysfunction following iminodipropionitrile administration in the rat.

The behavioral effects of 3,3'-iminodipropionitrile (IDPN) were studied using reflex modification of the acoustic startle response and figure-eight maze activity. A number of experiments were conducted with separate groups of adult male Long-Evans hooded rats exposed to saline or 50-500 mg/kg IDPN for 3 consecutive days. Auditory thresholds (reflex modification), motor activity, and grip strength were measured 1 day, and 1, 3, and 9 weeks postdosing. Reflex inhibition was monitored daily, prior to, during, and for 7 days following exposure. Auditory thresholds for 5- and 40-kHz tones were elevated approximately 25 dB and 50 dB, respectively. The onset of this auditory dysfunction in the 200-mg/kg/day group, as demonstrated by a loss of reflex inhibition, was 2 days for the 40-kHz tone and 4 days for the 5-kHz tone. Motor activity was increased up to 400% in the 200-mg/kg group, whereas there was no alteration in hindlimb grip strength. These data demonstrate dosage- and time-dependent alterations in auditory and motor function following IDPN exposure.

Acoustic Stimulation↗
PubMedDate not supplied

Interlaboratory comparison of motor activity experiments: implications for neurotoxicological assessments.

Motor activity is an important functional measure used in neurotoxicology. The effects of chemicals on motor activity, however, may depend on variables such as type of measurement apparatus, physical and environmental testing conditions, and many other experimental protocol and organismic variables. Due to the increasing use of motor activity in neurotoxicology, a major question concerns the potential for differences in experimental findings due to variations in sensitivity and reliability between different laboratories and devices used to measure motor activity. This study examined historical data from a number of laboratories that employed different devices and experimental protocols to measure motor activity. Four aspects of the motor activity data were compared: 1) within-laboratory control variability across time; 2) within-laboratory replicability of control data; 3) between-laboratory variability in the effects of chemicals; and 4) between-laboratory comparison of the control rates of habituation. The analyses indicated that there was a relatively restricted range of within-laboratory variability and reliability in control values, and that these ranges were comparable across laboratories. Similar profiles of habituation were also seen across the different laboratories. Moreover, in virtually every case, all laboratories were capable of detecting qualitatively similar changes in motor activity following acute exposure to a variety of chemicals. These data indicate a high degree of comparability in the data generated by the different devices and experimental protocols.

Animals↗
PubMedDate not supplied

Mid-frequency hearing loss in rats following inhalation exposure to trichloroethylene: evidence from reflex modification audiometry.

The present experiments were undertaken to characterize the hearing loss associated with 1,1,2-trichloroethylene (TCE) exposure. Adult male Long-Evans (LE) rats were exposed to TCE via inhalation (whole body) for 6 h/day for 5 days. The concentration-effect function (0-4000 ppm) was determined 3 weeks post-exposure. Animals were tested for auditory thresholds to 4, 8, 16, 24, 32, and 40-kHz tones using reflex modification audiometry. In a separate experiment, the time course of effects was determined by monitoring 16-kHz thresholds prior to, 1 h following each of the 5 exposure days, and 5 days, 1, 2, 4, 8, and 12 weeks post-exposure. At 14 weeks, these same animals were tested for thresholds to 0.5, 1, 2, 4, 8, 16, 24, 32, and 40-kHz tones. Results indicate elevated thresholds (hearing loss) for the 4000 ppm group at 8 and 16 kHz of approximately 18 and 30 dB, respectively. Time-course data demonstrated a rapid onset, a 20-dB loss at 16 kHz after the fifth exposure day, and a 40-dB loss by 2 weeks that persisted up to 14 weeks post-exposure. These data demonstrate an atypical and persistent, mid-frequency hearing loss in rats following inhalation exposure to TCE.

Administration, Inhalation↗
PubMedDate not supplied

Developmental neurotoxicity following neonatal exposure to 3,3'-iminodipropionitrile in the rat.

Adult exposure to the neurotoxicant 3,3'-iminodipropionitrile (IDPN), induces a hyperkinetic syndrome consisting of spontaneous head movements, abnormal circling, backward locomotion, and sensory disruption. We report here the behavioral effects of developmental exposure to IDPN in the rat. Animals were exposed (IP) to either saline, 75, 150, or 300 mg/kg/day on postnatal days (PND) 5-7. Animals were tested for: Figure-8 maze activity (PND 13-60); olfactory discrimination learning (PND 18 & 24); T-maze alternation and position discrimination learning (PND 25 & 26); acoustic startle response (PND 23, 61, & 62); passive avoidance (PND 70). To better define the dose response, a separate group of animals was exposed to either saline or 225 mg/kg/day (PND 5-7) and tested in the activity, T-maze, and startle paradigms. Animals exposed to 225 mg/kg/day and 300 mg/kg/day had decreased weight gain and lethality was 25% in the latter group. Signs of the IDPN syndrome, evident in the 225 and 300 mg/kg/day groups, persisted throughout the course of the study. IDPN exposed animals (300 mg/kg/day) were hyperactive on PND 17-60, failing to develop habituation in the Figure-eight maze until PND 60. The acoustic startle response was depressed for the 225 and 300 mg/kg/day groups on PND 23 only. Auditory thresholds were elevated for a high-frequency (40 kHz) but not a low-frequency tone (5 kHz) for the 225 and 300 mg/kg/day groups, indicating a hearing loss. IDPN treatment also disrupted performance of olfactory discrimination learning and produced cognitive deficits in T-maze learning in infants (300 mg/kg/day). That cognitive deficits also appeared in adulthood (PND 70) was demonstrated by learning deficits in a passive avoidance task at 150 and 300 mg/kg/day. IDPN (300 mg/kg/day) also caused a decrease in the wet weight of the whole brain (8%) and the cerebellum (12%) but not the hippocampus. These data demonstrate that short-term, neonatal exposure to IDPN in the rat produced persistent alterations in sensory, motor, and cognitive aspects of nervous system function.

Animals↗
PubMedDate not supplied

Implications of the use of neonatal birth weight, growth, viability, and survival data for predicting developmental neurotoxicity: a survey of the literature.

Current screening strategies for developmental neurotoxicants emphasize extensive behavioral and histological examination of the nervous system of maternally exposed offspring. In an ongoing effort to identify more rapid screening techniques which accurately predict developmental neurotoxicity, we conducted a literature review to investigate the suggestion that the Chernoff/Kavlock assay may adequately identify developmental neurotoxicants as well as developmental toxicants (58). We included information on a broad range of chemical classes including: pesticides, heavy metals, solvents, antiproliferative agents, and neuroactive drugs. For each chemical/agent, we recorded evidence of developmental neurotoxicity, teratological malformations of the nervous system, and associated information on the effects of that chemical on birth weight, growth, fetal viability, and/or neonatal survival (neonatal endpoints included in the Chernoff/Kavlock assay). Although complete Chernoff/Kavlock data were not always available, our results indicate that only 65% of developmental neurotoxicants affected at least one of the neonatal endpoints in the assay. Based on these results, we believe that reliance on the Chernoff/Kavlock assay as a primary developmental neurotoxicity screen could lead to a number of "false negatives" in hazard identification studies, and this assay should not be used to replace more comprehensive developmental neurotoxicity screening procedures.

Animals↗
PubMedDate not supplied

Effects of 3,3'-iminodipropionitrile on acquisition and performance of spatial tasks in rats.

3,3'-Iminodipropionitrile (IDPN) has been reported to disrupt learning and memory in rats (24). The present work addressed the effects of IDPN on tasks requiring the use of spatial information. Separate groups of male rats were dosed with IDPN (IP, in 1 ml/kg saline) for 3 consecutive days and tested in the following procedures: (a) step-through passive avoidance conditioning (0, 100, 150, and 200 mg/kg/day); (b) Morris water maze (MWM) acquisition and retention (0, 125, 150, 175, and 200 mg/kg/day); (c) radial arm maze (RAM) acquisition (0, 100, 200, and 400 mg/kg/day); (d) RAM steady-state performance (0, 200, and 400 mg/kg/day); (e) repeated acquisition in the RAM (0, and 200 mg/kg/day). The vestibular toxicity of IDPN resulted in alterations in spontaneous behavior or swimming deficits in 5 of 8 rats treated with 175 mg/kg/day and in all the animals dosed with 200 or 400 mg/kg/day. IDPN increased step-through PA latencies at 200 mg/kg/day but not at lower doses. In the MWM, no performance deficits were observed at the dose levels preserving the swimming ability of the animals. In both the acquisition and the steady-state RAM tasks, IDPN (400 mg/kg/day) induced an increase in both choice errors and perseverative errors. In the RAM repeated acquisition paradigm, IDPN (200 mg/kg/day) induced performance deficits that included a decreased rate of within-session reduction in errors. The present data show that IDPN disrupts performance of tasks requiring spatial learning and memory and indicate that these deficits can be in part caused by an acquisition deficit.

Animals↗
PubMedDate not supplied

Effects of toluene inhalation on detection of auditory signals in rats.

Inhalation of organic solvents can affect vigilance and reaction time in humans. An animal model of vigilance was designed to assess the effects of toluene on these processes. Adult male Long-Evans rats were trained to detect auditory signals (20-msec increases in the intensity of white noise). Two to 4 s after each signal (or blank period), two retractable levers were inserted into the test chamber. A press on one lever after a signal and on the other lever after a blank resulted in the delivery of food. Signal detection analysis showed that sensitivity (Sensitivity Index, SI) and response bias (Responsivity Index, RI) increased with signal intensity, indicating that loud signals were more detectable than soft signals and that the animals' criterion for responding "signal" increased with signal intensity. Response latency for correct choices was faster for signal trials than for blank trials. Toluene vapor was added to the airstream of these chambers at concentrations of 0, 1000, 1500, or 2000 ppm, either 10 or 30 min before testing and for the duration of each 1-h test. In air, SI increased across the duration of the test; this within-session improvement was reversed by toluene. RI did not change in air; it was decreased by toluene at the beginning of each exposure session, returned to the control level during exposure to 1000 and 1500 ppm toluene and exceeded air control after 40 min exposure to 2000 ppm toluene. Latency increased monotonically across toluene concentrations and time on test. Neither signal intensity nor the duration of toluene exposure before testing altered these effects of toluene. SI, RI, and latency baselines were recovered after toluene exposure indicating that no persistent effects of toluene were detectable. This conclusion was supported by data from other rats showing that toluene exposure (2000 ppm for 2 h/day for 4 consecutive days) did not affect auditory thresholds, as determined by reflex modification of an acoustic startle response using a 16 kHz tone as a prepulse stimulus, 7 or 17 days after exposure to toluene. Finally, rats tested immediately or 20 min after exposure to 0, 1000, 1500, or 2000 ppm toluene were not affected by the vapor, indicating that the impairment observed during toluene inhalation did not persist beyond the period of exposure.

Administration, Inhalation↗
PubMedDate not supplied

Vehicle and route dependent effects of a pyrethroid insecticide, deltamethrin, on motor function in the rat.

Deltamethrin is a potent neuroactive pyrethroid insecticide. Literature reports of the in vivo potency of deltamethrin, however, vary by greater than three orders of magnitude in studies employing numerous vehicles and routes of exposure. Therefore, the present study systematically compared IP and PO routes of exposure to deltamethrin (0.3-1000 mg/kg) delivered to adult rats in one of four different vehicles (corn oil, glycerol formal, Emulphor, or methylcellulose). A reduction in motor activity as measured in figure-8 mazes was used to index the potency of this pesticide on CNS function. Dose-effect and time-course determinations were made for each combination of vehicle and route. Results demonstrated that the potency of deltamethrin was dependent on both the route of administration and the vehicle. The ED50 for deltamethrin was 5.1 mg/kg when administered PO in corn oil, whereas, the ED50 was > 1000 mg/kg when administered PO in methylcellulose. Thus, reported discrepancies in the potency of deltamethrin on CNS function are at least partially attributable to route of administration and vehicle.

Administration, Oral↗
PubMedDate not supplied

Alterations in flash evoked potentials (FEPs) in rats produced by 3,3'-iminodipropionitrile (IDPN).

3,3'-Iminodipropionitrile (IDPN) is a neurotoxicant that produces changes in flash evoked potentials (FEPs) 18 weeks after treatment. We examined dose- and time-related effects of IDPN on FEPs at earlier time points than previously studied (52). Adult male Long-Evans rats were given IDPN (0, 100, 200, 400 mg/kg/day x 3 days, i.p.) and FEPs were recorded 14 days later. IDPN (400 mg/kg/day) decreased the amplitudes of some of the "early" and "middle" FEP peaks (n30 and N56), and increased the latencies of some early peaks (P21 and P46). A separate group of rats was treated with IDPN (0 or 400 mg/kg/day x 3 days, i.p.) and FEPs were recorded 1, 3, 7, 14, and 35 days later. The latencies of of all portions of FEPs were increased by IDPN, with maximal changes occurring at 7 and/or 14 days. The amplitude of the middle portions of FEPs (peaks N56, P63, N70, P90) were altered as early as day 3, and some changes were observed up to day 14. In contrast, the "late" portion of FEPs (peak N160) was affected at later times (days 14 and 35). Corneal opacities were noted on days 3 and 7, but were largely reversible by day 14. In the time-course study, IDPN decreased colonic temperature on days 1, 3, 7, and 14. The present results suggest that IDPN alters both the early FEP peaks related to the initial afferent sensory volley, and cortical processing associated with the middle and later portions of FEPs.

Animals↗
PubMedDate not supplied

A qualitative retrospective analysis of positive control data in developmental neurotoxicity studies.

Testing for neurodevelopmental effects commonly involves both functional and neuropathological assessments in offspring during and following maternal exposure. The use of positive controls in neurotoxicity screening has been advocated by numerous expert groups. Evaluation of positive control data allows evaluation of laboratory proficiency in detecting changes in the structure and function of the developing nervous system and comparison of the sensitivity of assessments in different studies and laboratories. This project surveyed approaches taken in contract and industrial laboratories in generating and providing these data. Positive control data submitted in support of 34 developmental neurotoxicity (DNT) studies from 16 different laboratories were summarized by test method for information on the following: age relevance of test subjects, the presence of a dose-response relationship, gender, group size, statistics, report quality, quality assurance, and the year the study was conducted. Endpoints included the following: developmental landmarks, clinical observations (CO), motor activity, startle response, learning and memory, qualitative neuropathology, and quantitative brain morphometry (linear measurements of selected brain regions). Results ranged from no positive control data for three laboratories, to one laboratory that submitted 17 separate positive control reports. The qualitative range was similarly broad, from excellent to poor. Various problems were identified, including the following: inappropriate report structure (e.g., copies of poster presentations), lack of individual data, inadequate methodological details, submission of very old data (>10 years) or data from completely different laboratories, use of inappropriate positive control chemicals or doses that were without effect, lack of statistical analysis, use of only one sex, and use of incompatibly aged animals. Analyses revealed that there were only 3 out of 16 laboratories that had submitted positive control data adequate for proficiency purposes for all of the major endpoints in the DNT study. Adequate positive control data are very useful in a weight-of-evidence approach to help determine the biological significance of results, and also to increase the confidence in negative results from DNT studies.

Animals↗
PubMedDate not supplied

Flash-, somatosensory-, and peripheral nerve-evoked potentials in rats perinatally exposed to Aroclor 1254.

Pregnant Long-Evans rats were exposed to 0, 1 or 6 mg/kg/day of Aroclor 1254 (A1254; Lot no. 124-191), a commercial mixture of polychlorinated biphenyls (PCBs), from gestation day (GD) 6 through postnatal day (PND) 21. At 128-140 days of age, male and female offspring were tested for visual-, somatosensory- and peripheral nerve-evoked potentials. The evoked responses increased in amplitude with larger stimulus intensities, and gender differences were detected for some endpoints. In contrast, developmental exposure to A1254 failed to significantly affect the electrophysiological measures. A subset of the animals were tested for low-frequency hearing dysfunction using reflex modification audiometry (RMA). An elevated threshold for a 1-kHz tone was observed, replicating previous findings of A1254-induced auditory deficits [Hear. Res. 144 (2000) 196; Toxicol. Sci. 45(1) (1998) 94; Toxicol. Appl. Pharmacol. 135(1) (1995) 77.]. These findings indicate no statistically significant changes in visual-, somatosensory- or peripheral nerve-evoked potentials following developmental exposure to doses of A1254 that produce behavioral hearing deficits. However, subtle changes in the function of the visual or somatosensory systems cannot be disproved.

Administration, Oral↗
PubMedDate not supplied

Schedule-controlled behavior in rats exposed perinatally to the PCB mixture Aroclor 1254.

Exposure to polychlorinated biphenyls (PCBs) has been shown to detrimentally affect learning and memory in children as well as schedule-controlled behavior in experimental animals. The objective of the present series of experiments was to extend research into the effects of PCBs on behavior maintained under both short (30 s) and long (5 min) fixed-interval (FI) schedules as well as an FI 3-min with reinforcement omission. Long-Evans rats were exposed to 0 or 6 mg/kg/day Aroclor 1254 (A1254) via oral gavage from Gestation Day 6 (GD 6) through Postnatal Day 21 (PND 21). At approximately PND 90, acquisition and steady-state performance were assessed under a series of FI reinforcement schedules consisting of FI 30-s, FI 5-min, and FI 3-min with 33% of the scheduled reinforcers omitted. Performance measures included index of curvature (IOC), response rate, and postreinforcement pause (PRP). There were no effects of A1254 on the acquisition of behavior under the FI 30-s schedule. Subsequently, there was an initial decrease in response rate and IOC and an increase in PRP following the transition from FI 30-s to the FI 5-min; there were, however, no treatment-related effects on any measure. During the reinforcement-omission procedure, there was an increase in the rate of responding and a decrease in IOC and PRP following omission intervals irrespective of treatment. These data are inconsistent with previous findings and suggest that perinatal A1254 exposure in the rat does not disrupt temporally organized behavior.

Animals↗