Detection of silver nanoparticles in cells by flow cytometry using light scatter and far-red fluorescence.

The cellular uptake of different sized silver nanoparticles (AgNP) (10, 50, and 75 nm) coated with polyvinylpyrrolidone (PVP) or citrate on a human derived retinal pigment epithelial cell line (ARPE-19) was detected by flow cytometry following 24-h incubation of the cells with AgNP. A dose dependent increase of side scatter and far red fluorescence was observed with both PVP and citrate-coated 50 nm or 75 nm silver particles. Using five different flow cytometers, a far red fluorescence signal in the 700-800 nm range increased as much as 100 times background as a ratio comparing the intensity measurements of treated sample and controls. The citrate-coated silver nanoparticles (AgNP) revealed slightly more side scatter and far red fluorescence than did the PVP coated silver nanoparticles. This increased far red fluorescence signal was observed with 50 and 75 nm particles, but not with 10 nm particles. Morphological evaluation by dark field microscopy showed silver particles (50 and 75 nm) clumped and concentrated around the nucleus. One possible hypothesis to explain the emission of far red fluorescence from cells incubated with silver nanoparticles is that the silver nanoparticles inside cells agglomerate into small nano clusters that form surface plasmon resonance which interacts with laser light to emit a strong far red fluorescence signal. The results demonstrate that two different parameters (side scatter and far red fluorescence) on standard flow cytometers can be used to detect and observe metallic nanoparticles inside cells. The strength of the far red fluorescence suggests that it may be particularly useful for applications that require high sensitivity. © Published 2013 Wiley-Periodicals, Inc.

Detection of TiO2 nanoparticles in cells by flow cytometry.

Evaluation of the potential hazard of man-made nanomaterials has been hampered by a limited ability to observe and measure nanoparticles in cells. In this study, different concentrations of TiO(2) nanoparticles were suspended in cell culture medium. The suspension was then sonicated and characterized by dynamic light scattering and microscopy. Cultured human-derived retinal pigment epithelial cells (ARPE-19) were incubated with TiO(2) nanoparticles at 0, 0.1, 0.3, 1, 3, 10, and 30 microg/ml for 24 hours. Cellular reactions to nanoparticles were evaluated using flow cytometry and dark field microscopy. A FACSCalibur flow cytometer was used to measure changes in light scatter after nanoparticle incubation. Both the side scatter and forward scatter changed substantially in response to the TiO(2). From 0.1 to 30 microg/ml TiO(2), the side scatter increased sequentially while the forward scatter decreased, presumably due to substantial light reflection by the TiO(2) particles. Based on the parameters of morphology and the calcein-AM/propidium iodide viability assay, TiO(2) concentrations below 30 microg/ml TiO(2) caused minimal cytotoxicity. Microscopic analysis was done on the same cells using an E-800 Nikon microscope containing a xenon light source and special dark field objectives. At the lowest concentrations of TiO(2) (0.1-0.3 microg/ml), the flow cytometer could detect as few as 5-10 nanoparticles per cell due to intense light scattering by TiO(2). Rings of concentrated nanoparticles were observed around the nuclei in the vicinity of the endoplasmic reticulum at higher concentrations. These data suggest that the uptake of nanoparticles within cells can be monitored with flow cytometry and confirmed by dark field microscopy. This approach may help fulfill a critical need for the scientific community to assess the relationship between nanoparticle dose and cellular toxicity Such experiments could potentially be performed more quickly and easily using the flow cytometer to measure both nanoparticle uptake and cellular health.

The comparability of rat and human visual-evoked potentials.

A series of experiments addressed the issue of comparability among neurological processes in pigmented rat and human visual systems. In the first set of experiments, transient visual-evoked potentials (VEPs) were elicited by the onset of sine-wave gratings of various spatial frequencies. The spatial frequency-response profiles of the first positive and immediately succeeding negative components differed from one another, but were similar in the two species. In addition, amplitude of the negative, but not the positive, component was strongly attenuated in both species following stationary pattern adaptation. In the second set of experiments, steady-state VEPs were elicited by the onset and offset of the gratings. The spatial frequency profiles of the 1F (response amplitude at the frequency of stimulus onset-offset) and 2F response components differed from one another, but were similar in both species. The final set of experiments indicated that diazepam, a GABA agonist, reduced amplitude of 2F, but not 1F, in both species. These results suggested that at least some functional subsystems mediating spatial vision in humans may have qualitatively similar counterparts in rats.

Quantitative methods for cross-species mapping (CSM).

Cross-species extrapolation will be defined as prediction from one species to another without empirical vetification. Cross-species mapping (CSM) is the same except empirical vetification is performed. CSM may be viewed as validation of methods for extrapolation. Algorithms for CSM may originate from theory, from empirical observations or a combination of the two. Regardless of their origins, CSM algorithms must be explicated and confidence intervals given around their predictions. This paper offers a quantitative method for constructing CSM equations which is useful in evaluation of the CSM and as an aid in the design of new experiments in CSM and extrapolation. The method requires fitting mathematical models for the physiological or behavioral phenomena to be mapped across species. A CSM equation can then be derived from the models in each species and approximate confidence limits may be obtained for predictions from the equation. The method is useful even when the models in the two species differ in form, implying differences in physiology or behavioral principles between species. The method proposed has a number of remaining uncertainties and possible problems.

Body temperature-dependent and independent actions of chlordimeform on visual evoked potentials and axonal transport in optic system of rat.

Pattern-reversal-evoked potentials (PREPs), flash-evoked potentials (FEPs), rapid axonal transport in the optic system and body temperature were measured in hooded rats, treated with either saline or the formamidine insecticide/acaricide, chlordimeform (CDM). Rats receiving chlordimeform had low body temperatures when housed at standard laboratory room temperature, 22 degrees C, but not at 30 degrees C. Peak latencies of flash-evoked potentials were prolonged by chlordimeform at 22 degrees C, but not at 30 degrees C. The rate of axonal transport was slowed in chlordimeform-treated hypothermic rats, but not in chlordimeform-treated warmed rats. These findings suggest that the flash-evoked potential and axonal transport changes produced by chlordimeform were an indirect consequence of hypothermia. In contrast, chlordimeform increased pattern-reversal evoked potential peak latencies and peak-to-peak amplitudes independent of body temperature. These findings confirm and extend previous reports of chlordimeform-induced hypothermia, emphasize the importance of changes in body temperature as a possible confounding factor in studies of neuroactive agents and demonstrate that chlordimeform has both body-temperature-dependent and independent actions in the visual system in the rat.

Monoamine oxidase inhibition cannot account for changes in visual evoked potentials produced by chlordimeform.

Chlordimeform (CDM), a formamidine insecticide and monoamine oxidase (MAO) inhibitor, has recently been shown to produce large changes in visual evoked potentials of hooded rats (Boyes and Dyer, 1984a). Two experiments were performed to determine if the changes in evoked potentials were a result of the inhibition of MAO. In the first, the degree of inhibition of MAO in the brains of rats treated with chlordimeform (1.0-100 mg/kg, i.p.) was compared with that produced by pargyline (0.3-30 mg/kg, i.p.). Both compounds preferentially inhibited MAO-B, although MAO-A was substantially inhibited at larger doses. Pargyline was a relatively more potent inhibitor of MAO than chlordimeform, but not more efficacious. In the second experiment, pattern reversal evoked potentials (PREPs) and flash-evoked potentials (FEPs) were recorded from groups of rats after treatment with either saline, 0.4 mg/kg pargyline, 20 mg/kg pargyline or 40 mg/kg chlordimeform. The latter two groups were selected so as to have similar levels of inhibition of MAO, about 90% inhibition of MAO-B and 60% inhibition of MAO-A. The results showed a doubling of the amplitude of pattern reversal evoked potentials and increased latencies of the pattern reversal evoked potential and the flash-evoked-potentials in the chlordimeform-treated group, but no significant changes from saline control values in the pargyline-treated groups. These results confirm that chlordimeform is a MAO inhibitor at doses which produce behavioral and electrophysiological changes, but demonstrate further that the changes in visual evoked potentials produced by chlordimeform are not a direct result of the inhibition of MAO.

The organophosphate pesticide chlorpyrifos affects form deprivation myopia.

PURPOSE: The effects of the anti-cholinesterase organophosphate pesticide chlorpyrifos (CPF) on the refractive development of the eye were examined. Form deprivation was used to induce eye growth to address the previously reported relationship between organophosphate pesticide use and the incidence of myopia. METHODS: Chickens, a well-established animal model for experimental myopia and organophosphate neurotoxicity, were dosed with chlorpyrifos (3 mg/kg per day, orally, from day 2 to day 9 after hatching) or corn oil vehicle (VEH) with or without monocular form deprivation (MFD) over the same period. The set of dependent measures included the refractive state of each eye measured using retinoscopy, axial dimensions determined with A-scan ultrasound, and intraocular pressure. RESULTS: Dosing with CPF yielded an inhibition of 35% butyrylcholinesterase in plasma and 45% acetylcholinesterase in brain. MFD resulted in a significant degree of myopia in form-deprived eyes resulting from significant lengthening of the vitreal chamber of the eye. CPF significantly reduced the effect of MFD, resulting in less myopic eyes (mean refraction: VEH-MFD = -16.2 +/- 2.3 diopters; CPF-MFD = -11.1 +/- 1.8 diopters) with significantly shorter vitreal chambers. Nonoccluded eyes were, on average, slightly hyperopic. Treatment with CPF for 1 week in the absence of MFD led to no significant change in ocular dimensions or refraction relative to controls. CONCLUSIONS: The use of form deprivation as a challenge suggests that CPF treatment interferes with the visual regulation of eye growth.

Neurotoxic and pharmacokinetic responses to trichloroethylene as a function of exposure scenario.

Strategies are needed for assessing the risks of exposures to airborne toxicants that vary over concentrations and durations. The goal of this project was to describe the relationship between the concentration and duration of exposure to inhaled trichloroethylene (TCE), a representative volatile organic chemical, tissue dose as predicted by a physiologically based pharmacokinetic model, and neurotoxicity. Three measures of neurotoxicity were studied: hearing loss, signal detection behavior, and visual function. The null hypothesis was that exposure scenarios having an equivalent product of concentration and duration would produce equal toxic effects, according to the classic linear form of Haber's Rule ((italic)C(/italic) times t = k), where C represents the concentration, t, the time (duration) of exposure, and k, a constant toxic effect. All experiments used adult male, Long-Evans rats. Acute and repeated exposure to TCE increased hearing thresholds, and acute exposure to TCE impaired signal detection behavior and visual function. Examination of all three measures of neurotoxicity showed that if Haber's Rule were used to predict outcomes across exposure durations, the risk would be overestimated when extrapolating from shorter to longer duration exposures, and underestimated when extrapolating from longer to shorter duration exposures. For the acute effects of TCE on behavior and visual function, the estimated concentration of TCE in blood at the time of testing correlated well with outcomes, whereas cumulative exposure, measured as the area under the blood TCE concentration curve, did not. We conclude that models incorporating dosimetry can account for differing exposure scenarios and will therefore improve risk assessments over models considering only parameters of external exposure.

A dosimetric analysis of behavioral effects of acute toluene exposure in rats and humans.

The literature on behavioral effects of exposure to toluene is difficult to assess due, in part, to a wide variety of exposure conditions employed and outcomes measured. This study investigated whether previous experiments would be more consistent with each other if toluene exposure parameters were expressed not as concentration and duration, but as estimated amount of toluene in tissues. A physiologically based pharmacokinetic (PBPK) model was used to estimate concentration of toluene in arterial blood (CaTOL) from published studies in rats and humans exposed acutely to toluene vapor. Data for rats were selected from studies of avoidance behavior using both rate of responding and measures of successful responding. Data for humans were from studies of choice reaction time (CRT). Behavioral measures were converted to proportion of baseline to place them on a common scale across experiments. A meta-analysis was done to fit dose-effect curves using CaTOL and the rescaled effects. Results demonstrated that effects were an orderly function of CaTOL and were not influenced by concentration or duration of exposure, except as exposure influenced CaTOL. In rats, response rates first increased, reached a peak, and then declined as CaTOL increased. Successful avoidance in rats and CRT in humans always declined as CaTOL increased. In rats, response rates were increased by 10% at CaTOL approximately 13 ml/L. In humans, reaction times increased by 10% at CaTOL approximately 3 ml/L. Cross-species comparisons were made with the following caveats: PBPK uncertainties, few human data, and poor task comparability.

A physiologically based pharmacokinetic model for trichloroethylene in the male long-evans rat.

A physiologically based pharmacokinetic (PBPK) model for trichloroethylene (TCE) in the male Long-Evans (LE) rat was needed to aid in evaluation of neurotoxicity data collected in this rodent stock. The purpose of this study was to develop such a model with the greatest possible specificity for the LE rat. The PBPK model consisted of 5 compartments: brain, fat, slowly perfused tissue, rapidly perfused viscera, and liver. Partition coefficients (blood, fat, muscle, brain, liver) were determined for LE rats. The volumes of the brain, liver, and fat compartments were estimated for each rat, with tissue-specific regression equations developed from measurements made in LE rats. Vapor uptake data from LE rats were used for estimation of Vmaxc. As blood flow values for LE rats were not available, values from Sprague-Dawley (SD) and Fischer-344 (F344) rats were used in separate simulations. The resulting values of Vmaxc were used to simulate tissue (blood, liver, brain, fat) TCE concentrations, which were measured during (5, 20, 60 min) and after (60 min of TCE followed by 60 min of air) flow-through inhalation exposures of LE rats to 200, 2000, or 4000 ppm TCE. Simulation of the experimental data was improved by use of F-344 blood-flow values and the corresponding Vmaxc (8.68 mg/h/kg) compared to use of SD flows and the associated Vmaxc (7.34 mg/h/kg). Sensitivity analysis was used to determine those input parameters with the greatest influence on TCE tissue concentrations. Alveolar ventilation consistently (across exposure concentration, exposure duration, and target tissue) had the greatest impact on TCE tissue concentration. The PBPK model described here is being used to explore the relationship between measures of internal dose of TCE and neurotoxic outcome.

Hypothermia and chloropent anesthesia differentially affect the flash evoked potentials of hooded rats.

Anesthetics and body temperature alterations are both known to alter parameters of sensory-evoked responses. However few studies have quantitatively assessed the contributions of hypothermia to anesthetic-induced changes. Two experiments were performed. In the first, chronically implanted rats were injected with either 0, 0.05, 0.10 or 0.20 ml Chloropent/100 g b.w., while body temperature was maintained. Flash evoked potentials recorded 30 min later showed increased latencies but only minor (not statistically significant) changes in amplitude. In the second experiment the same rats were anesthetized with 0.35 ml Chloropent/100 g b.w. and rectal temperature was systematically varied between 31 degrees C and 37 degrees C. Over the ranges of temperature and anesthetic employed, latencies increased more extensively with hypothermia than with anesthesia. P1N1 amplitude doubled when temperature was lowered to 31C, but P2N2 and N2P3 amplitudes declined over the same temperature range. Anesthetic-induced changes in peak-to-peak amplitude did not reach statistical significance when body temperature was constant. The findings suggest that previously reported alterations in evoked potentials following anesthesia may have been confounded with hypothermia.

Pattern reversal visual evoked potentials in awake rats.

A method for recording pattern reversal evoked potentials (PREPs) from awake restrained rats has been developed. The procedure of Onofrj et al. [26] was modified to eliminate the need for anesthetic, thereby avoiding possible interactions of the anesthetic with other manipulations of interest. Rats were restrained in a harness and placed in front of a pattern generating TV screen displaying a black and white alternating square wave grating. Using various stimulation and recording parameters, normative data are presented from 141 adult male Long-Evans hooded and 11 adult male Sprague-Dawley albino rats. Reliable waveforms were recorded with five identifiable peaks. The labels and mean latencies of these peaks in hooded rats were: N1, 47.3 msec; P1, 65.7 msec; N2, 83.3 msec; P2, 94.4 msec; and N3, 129.8 msec. Spatial acuity functions generated with PREPs gave acuity estimates which corresponded closely to values determined behaviorally for hooded and albino rats [4,11].

Surface distribution of flash-evoked and pattern reversal-evoked potentials in hooded rats.

Simultaneous recording from 21 electrode sites in a 4 X 4 mm area over the posterior cortex was used to determine the surface distribution of all major peaks which constitute flash-evoked potentials (FEPs) and pattern reversal evoked-potentials (PREPs) in hooded rats. Topographical maps were constructed with respect to Bregma and midline reference points. The data indicate that not all of the peaks which constitute either evoked potential have their greatest amplitude within the classically defined primary visual cortex. Further, since the FEPs were produced by uniform stimulation, the data suggest that surface regions of the rat visual cortex differ in ways other than simply the portion of the visual field from which information is received.

A comparison of Haber's rule at different ages using a physiologically based pharmacokinetic (PBPK) model for chloroform in rats.

Haber's rule as commonly interpreted in inhalation toxicology, can be stated as exposure concentration times duration equals a constant biological effect, or C x t=k. In other words, identical products of concentration and duration lead to the same effect. The goals of this paper are to develop a biological and pharmacokinetic modeling approach for chloroform, and to evaluate Haber's rule for different ages by taking into account the physiological changes due to growth and aging in rats. Three-dimensional dose-response surfaces for liver toxicity were generated for each age group of interest: adolescent, adult, and senescent rats. The three-dimensional surfaces were then characterized with a generalized description of Haber's rule for each age group. The simulations suggest that adolescent rats need higher exposure levels in order to achieve similar levels of liver damage compared to adults or senescent rats, if the comparison is made using the same exposure length. In summary, a pharmacokinetic modeling approach with a biological framework including the chemical's mode of action, was used to relate concentration, exposure duration and effect. Major advantages of this approach include: the potential ability to extrapolate to humans, the inclusion of aging in the simulations, and the ability to summarize the results using a generalized form of Haber's rule.

Combined effects of paired solvents on the rat's auditory system.

A number of volatile organic solvents have been shown to be ototoxic to rats, but there is little information regarding how solvents might act in this way when encountered in combination. To examine this issue, male Long Evans rats were exposed by inhalation to pairs of solvents known to be ototoxic when administered individually; those reported on here are trichloroethylene+toluene, mixed xylenes+trichloroethylene, xylenes+chlorobenzene, and chlorobenzene+toluene. Rats were exposed 8 h/day for 5 consecutive days, using complementary proportions of isoeffective concentrations of the solvents alone. Hearing was assessed by brainstem-evoked response audiometry. The effects were as predicted by a linear dose-addition model, indicating additive rather than synergistic or antagonistic interactions at the concentrations studied.

Rat and human sensory evoked potentials and the predictability of human neurotoxicity from rat data.

The development of comprehensive quantitative models as alternatives to risk assessment based on uncertainty factors will require many steps, among them consideration of the relationships between the health endpoints which are measured in laboratory animals and humans. Sensory evoked potentials are measures of sensory function which can be recorded from many species, including humans, and as such provide an opportunity for examining the extrapolation of neurotoxicity data from laboratory animals to humans. Our research strategy for investigating how well laboratory rat data predict human neurotoxic risk involves comparing parametric stimulus manipulations and drug treatments in both species. Finally, we are comparing results in humans with neurodegenerative conditions, including those induced by neurotoxicant exposure, with animal models. To date, we have focused on pattern-elicited visual evoked potentials (VEPs) recorded from pigmented rats and humans. Parametric manipulations of spatial frequency, temporal frequency and stimulus contrast revealed parallel functions, displaced for differences in absolute sensitivity. Additionally, diazepam produced similar effects in rats and human volunteers. A quantitative cross-species map was developed to illustrate the prediction of human effects from rat data. Exposure to carbon disulfide produced changes in rat VEP-derived contrast sensitivity functions, which resembled psychophysically-measured loss of visual contrast sensitivity in human workers exposed to organic solvents. The results of these continuing efforts should help indicate how well animal electrophysiological measures predict human neurotoxicity.

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.

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.

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.

Rat and human visual-evoked potentials recorded under comparable conditions: a preliminary analysis to address the issue of predicting human neurotoxic effects from rat data.

Pattern-onset visual-evoked potentials (VEPs) were recorded from rats and humans in order to perform cross-species comparison of neuronal functional properties reflected by the early VEP components. The spatial frequency of a sinusoidal test grating was varied in Experiment 1. For both species, amplitude of the first positive VEP component was larger at low spatial frequency and decreased as spatial frequency increased. The immediately succeeding negative component was small at low spatial frequency and was of maximal amplitude at moderate spatial frequency. The effects of stationary pattern adaptation on these components were investigated in Experiment 2. Subjects viewed either a blank field or the test grating prior to recording VEPs. For both species, adaptation had no effect on the positive component but strongly attenuated the negative component. Experiment 3, in which only humans were tested, indicated that the negative component was of cortical origin. Only cortical neurons are known to be orientation selective, and the effect of adaptation diminished as the orientation difference between the adaptation and test gratings increased. These results suggest that the early positive and negative components arise from parallel visual pathways, and that the rat components may reflect visual processes qualitatively similar to those of humans.