In memoriam: Robert W. Bell, November 22, 1931- September 16, 2000.
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Biomedical subjects
Publications and source records attributed to N K Laughlin.
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Seventy-two female rhesus monkeys were randomly assigned to three lead exposure conditions (none, birth to 1 year, birth to 2 years). In a completely crossed design, the lead-exposed and control monkeys were randomized to placebo or chelation therapy which began at 1 year of age. Dosing was conducted daily beginning on day 8 postpartum. The lead dose levels were adjusted biweekly to gradually elevate the blood lead level of each monkey to a target of 1.69-1.93 micromol/L (35-40 microg/dL). Succimer (or placebo) was administered orally (30 mg/kg/day for 5 days and 20 mg/kg/day for 14 additional days) for a total 19-day treatment regimen. There were two separate chelation regimes at 53 and 65 weeks of age. Succimer therapy in combination with lead abatement reduced blood lead levels significantly faster than lead abatement alone; however, that advantage disappeared once succimer therapy was discontinued. Weight, crown-rump length, and head circumference were measured regularly. Growth in weight, length, and head circumference did not vary significantly as a function of blood lead levels. Succimer chelation therapy did not significantly affect weight, length, or head circumference through 2 years of age.
Although succimer (Chemet, meso-2,3-dimercaptosuccinic acid, DMSA) is considered to be a safe and effective chelating agent for the treatment of lead poisoning in humans, there is concern that it may increase the gastrointestinal (GI) absorption and retention of Pb from exposures suffered concurrent with treatment. This concern is justified because the availability of Pb-safe housing during outpatient treatment with oral succimer is limited. We used a juvenile nonhuman primate model of moderate childhood Pb intoxication and a sensitive double stable Pb isotope tracer methodology to determine whether oral succimer chelation affects the GI absorption and whole-body retention of Pb. Infant rhesus monkeys (n = 17) were exposed to Pb daily for 1 year postpartum to reach and maintain a target blood lead (BPb) level of 35-40 microg/dL. Animals were administered succimer (n = 9) or vehicle (n = 8) over two successive 19 day succimer treatment regimens beginning at 53 and 65 weeks of age. The present study was conducted over the second chelation regimen only. Animals received a single intravenous (iv) dose of stable (204)Pb tracer (5 microg, 24.5 nmol) followed by a single oral dose of stable (206)Pb tracer (72.6 microg, 352 nmol) immediately before chelation, in order to specifically evaluate GI Pb absorption and whole-body Pb retention with treatment. We collected complete urine and fecal samples over the first 5 days and whole blood over the first 8 days of treatment for analyses of stable Pb isotopes using magnetic sector inductively-coupled plasma mass spectrometry. Results indicate that succimer significantly reduced the GI absorption of Pb (vehicle, 64.9% +/- 5.5; succimer, 37.0% +/- 5.8; mean +/- SEM). Succimer also significantly increased the urinary excretion of endogenous Pb by approximately 4-fold over the vehicle treatment, while endogenous fecal Pb excretion was decreased by approximately 33%. Finally, although succimer reduced the whole-body retention of endogenous Pb by approximately 10% compared to vehicle, the majority (77%) of the administered internal dose of Pb tracer was retained in the body when assessed after 5 days of treatment. These data do not support the concern that succimer treatment increases GI Pb absorption.
Myeloid neoplasia has been studied extensively in human beings but has not been reported in macaques. A 2-year-old female rhesus macaque that was experimentally exposed to lead as a neonate, was noted to have immature circulating myelocytic cells, including 1% blasts, and normocytic normochromic anemia on a blood sample obtained for monthly health monitoring. The animal was treated with hydroxyurea, blood transfusion, and recombinant human erythropoietin to reduce the leukocytosis and correct the anemia. The disease had a relatively indolent course for 3 months, when it progressed to blast crisis. After the onset of blast crisis, the animal was euthanized because of bleeding problems, anemia, and a progressive decline in her health. The animal was negative by serology, polymerase chain reaction (PCR) assays, and/or culture for simian retrovirus (SRV), simian T-lymphotropic virus type I (STLV-I), and simian immunodeficiency virus (SIV). PCR assay for the bcr-ABL chromosomal translocation using primers made for the human gene was negative. Serology for Epstein-Barr virus (EBV)-like viruses was positive for IgG directed against the viral nucleocapsid antigen, but epidemiologic factors make it unlikely that the leukemia was associated with EBV-induced viral transformation. Lead exposure has been associated with neoplasia in human beings, and the possible role of neonatal lead exposure in hematologic neoplasias deserves further scrutiny.
The extent to which succimer (2,3-dimercaptosuccinic acid, DMSA) chelation reduces target organ lead (Pb) levels, including the skeleton, relative to the cessation of Pb exposure is a primary consideration in evaluating its efficacy for reducing toxicity in children. Here, we utilized a rhesus monkey model of childhood Pb exposure and a sensitive stable (204)Pb isotope tracer methodology to determine the efficacy of succimer for reducing Pb in blood, liver, and skeletal tissues from chronic (>/=1 year) versus short-term (3-4 days) Pb exposures. Specific attention was paid to the efficacy of succimer treatment compared to the cessation of Pb exposure. Infant rhesus monkeys (n = 48) were exposed to Pb daily for 1 year or >1 year postpartum to reach and maintain a target blood Pb level of 35-40 microg/dL. Two successive 19-day succimer treatment regimens were administered at 53 and 65 weeks of age (30 mg/kg/day x 5 days followed by 20 mg/kg/day x 14 days). Blood was collected over the course of treatment, and liver and bone biopsy samples were collected on days 0, 5, and 20, relative to the start of treatment (day 0). Complete 24-h urine collections were conducted over the course of treatment. Results of the first chelation indicate that a single regimen of succimer treatment led to significant reductions in blood and liver Pb levels, relative to the placebo group. However, the cessation of Pb exposure alone (i.e., placebo) also led to significant reductions in blood and liver compared to pretreatment levels. Neither succimer nor the cessation of Pb exposure had a significant impact on bone lead levels. Blood Pb levels in the succimer-treated group rebounded within 5 days after treatment ended, becoming comparable with levels in the placebo group from that point on. Results from the second chelation indicate that succimer treatment is essentially equally efficacious in reducing blood Pb at moderate (20 microg/dL) levels where exposures ended >3 months previously and more elevated (40-50 microg/dL) levels where exposures ended just prior to treatment, relative to the placebo treatment. Finally, similar overall outcomes were observed for tissue Pb from recent exposures (i.e., (204)Pb tracer levels), indicating little or no apparent difference in the chelation of Pb from recent (3-4 days) versus long-term exposures. These data demonstrate that succimer does not reduce skeletal Pb levels, and they show that the efficacy of succimer for reducing blood Pb levels does not persist beyond the completion of treatment due to posttreatment rebounds in blood Pb from endogenous sources. They also demonstrate the relative benefit of eliminating Pb exposures, which serves to underscore the importance of primary prevention of Pb exposure. The extent to which these data reflect the efficacy of succimer for reducing neurocognitive impairment is not yet known, although those data are forthcoming.
Succimer is considered to be a safe and effective treatment for lead (Pb) poisoning, since it reduces body Pb levels without an apparent diuresis of other essential elements. However, while existing clinical data indicate that succimer does not significantly increase the excretion of non-target elements, those studies have also reported a wide range of outcomes. Therefore, we investigated whether succimer treatment measurably increased the urinary excretion of essential elements in a primate model of childhood Pb exposure. Infant rhesus monkeys (Macaca mulatta) were exposed to Pb from birth through one year of age, and presented blood Pb levels of approximately 40-50 microg/dL at the start of treatment. Subsequently, they were treated with succimer (30 mg/kg/day x 5 days followed by 20 mg/kg/day x 14 days, n = 15) or vehicle (n = 14) for 19 days. Complete urine samples were collected over the first 5 days of treatment, and were analyzed for levels of calcium (Ca), cobalt (Co), copper (Cu), iron (Fe), lead (Pb), magnesium (Mg), manganese (Mn), nickel (Ni), and zinc (Zn), using trace metal-clean techniques and magnetic sector-ICP-MS. Succimer treatment significantly (p < 0.05) reduced blood Pb levels when compared to the vehicle group over the treatment period, and concomitantly produced a significant >4-fold increase in urinary Pb excretion. Succimer treatment also significantly (p < 0.05, multivariate ANOVA) increased the urinary excretion of essential elements, but only when the cumulative total excretion over treatment days 1-5 for all elements were considered. None of these relative increases reached statistical significance for any particular element x day, although increases in Zn (day 3) excretion were only marginally non-significant (0.1 > p > 0.05). Multivariate analyses of a subset of elements (Cu, Fe, Mn, Zn) similarly indicated no significant effect of succimer treatment overall, although the urinary excretion of Mn was significantly increased on day 3 of treatment. Collectively, these data indicate that succimer does contribute to an increase in the urinary excretion of essential elements, although not significantly for any single element considered here. This may be important in Pb-exposed children, who can possess reduced trace element reserves due to nutritional deficiencies.
The extent to which succimer (meso-2,3-dimercaptosuccinic acid [DMSA], Chemet) reduces brain lead (Pb) levels may be a primary consideration in evaluating its efficacy for reducing neurotoxicity. Clinical research in this area has been hampered by the need to use blood Pb levels as the index of treatment efficacy, despite the fact that brain Pb level is the exposure parameter of greater relevance to cognitive outcomes. Here, a nonhuman primate model of human Pb exposure was used to determine: (1) The efficacy of oral succimer for reducing brain Pb derived from chronic or recent exposures, and (2) The extent to which blood Pb levels reflect brain Pb prior to and following chelation. Adult rhesus monkeys were chronically exposed to Pb orally for 5 weeks to reach and maintain a target blood Pb level of 35-40 microg/dL. Chelation of Pb from recent exposures was assessed using a stable (204)Pb isotope tracer administered over 4 days prior to treatment. Immediately prior to chelation, a prefrontal cortex (PFC) biopsy was collected to determine pretreatment brain Pb levels. Subsequently, monkeys were assigned to vehicle (n = 5) or succimer (n = 6, 30 mg/kg/day x 5 days followed by 20 mg/kg/day x 14 days) groups. Blood and brain PFC, frontal lobe (FL), hippocampus (H), and striatum (S) were analyzed for total Pb and (204)Pb tracer concentrations by magnetic sector inductively coupled plasma-mass spectrometry. There were no measurable differences in brain Pb concentrations between the succimer and vehicle groups, indicating that succimer treatment was not efficacious in reducing brain Pb levels. In contrast, the cessation of Pb exposure significantly reduced brain (PFC) Pb ( approximately 34%) when compared to pretreatment levels (succimer and vehicle groups). Pb concentrations also varied among brain regions (PFC > FL approximately H > S). Finally, pretreatment PFC Pb concentrations were significantly correlated with the integrated blood Pb level (AUC) over the Pb exposure period, but not with the single pretreatment blood Pb collected concurrently with the PFC biopsy. Following treatment, blood Pb levels correlated only with Pb in the PFC, and not the other brain regions measured (FL, H, S). These data indicate that, under the conditions of this study, succimer treatment did not reduce brain Pb levels beyond the cessation of Pb exposure alone. Moreover, a single blood Pb measurement may be a poor predictor of brain Pb levels, reflecting limitations in the use of blood Pb level as an indicator of treatment efficacy.
Distortion product otoacoustic emission (DPOAE), auditory brainstem evoked response (ABR), and behavioral thresholds were recorded in a group of 15 adult rhesus monkeys with normal auditory function. DPOAE thresholds were recorded with stimulus parameters selected to maximize signal-to-noise ratio. Additional averaging at the lowest frequencies ensured comparable noise levels across frequencies. DPOAE thresholds decreased with increasing frequency (f(2)=0.5-16 kHz) and at 16 kHz were close to 0 dB SPL. ABR thresholds were best from 1 through 16 kHz (32-38 dB peSPL); higher at 0.5 (45 dB peSPL), 24 (39 dB peSPL), and 30 kHz (49 dB peSPL). At all levels including threshold, the early ABR waves (II and I) were more prominent at the high frequencies while the later waves (IV and V) were more prominent at the low frequencies. The behavioral thresholds recorded were similar to those reported by other researchers although elevated by about 10 dB presumably because of the complexity of the threshold task. DPOAE and ABR thresholds can be reliably and efficiently recorded in the rhesus monkey and provide information concerning site of processing in the auditory pathway not directly available from behavioral data.
During the past two years, the National Institutes of Health have made significant changes in the review process for investigator-initiated research grant applications in neurotoxicology. First, study sections that formerly dealt with toxicology and alcohol, respectively, have been merged. Neurotoxicology grant applications are now reviewed by ALTX-3, a study section in which the majority of members have expertise in the neuronal, biochemical or behavioral effects of alcohol, but usually not other neurotoxicants. Second, the NIH has instituted new review criteria, in which significance, approach, innovation, investigator expertise, and research environment must all be explicitly addressed by the reviews. In this article, past and present members of the ALTX-3 study section describe the NIH review process, with emphasis on how neurotoxicology applications are handled, and provide guidelines for preparing competitive applications.
Auditory event related potentials were recorded from neonatal, 3-month, and 3-year old rhesus monkeys. Auditory brainstem evoked responses (ABRs) were reliably recorded at all ages. ABR latencies decreased with age. Age effects were greater the more centrally generated the wave. Wave I amplitude decreased with age, Wave II increased, and Wave IV remained about the same. Stimulus rate effects were greater in neonates than older monkeys. Stimulus frequency also affected the ABR, but not differentially as a function of age. Recording montage had a significant effect on the recorded waveform. Wave I tended to be larger in amplitude in horizontal recordings and front-back recordings, while the later waves were relatively more prominent in more vertical montages. Middle latency evoked responses and late potentials were less reliably recorded than the ABR. Their reproducibility improved with age. Auditory event related potentials are promising measures of auditory function for research requiring nonhuman primate models of the developing human.
A geriatric rhesus monkey (Macaca mulatta) population, previously exposed to lead, was investigated using 109Cd K X-ray fluorescence (K XRF) to determine whether metabolism of lead in bone was similar to that in human populations. The accumulation rate of lead into the tibia in this group of monkeys was determined to be 0.10-0.13 micrograms Pb (g bone mineral)-1 (microgram dl-1 year)-1, which compares well with human data, where the rate has been found to be 0.05-0.10 microgram Pb (g bone mineral)-1 (microgram dl-1 year)-1. In addition, bone lead changes over a 10-month time period were investigated, but no statistically significant difference was found. A halflife for lead in "bone" was calculated by fitting a single exponential model to serial blood lead data; the mean half-life of lead in bone was found to be 3.0 +/- 1.0 years. Both endogenous and exogenous lead exposure were found to be low at the present time, 10 years after cessation of lead intake. It is concluded that rhesus monkeys are an extremely good animal model of human bone lead metabolism and, in addition, that further research is needed to provide a more complete understanding of lead metabolism in geriatric populations.
Distortion product otoacoustic emissions (DPOAEs) were compared in eight rhesus monkeys (Macaca mulatta) and eight normal hearing humans. DPOAEs were recorded in three conditions. In the first condition, DPOAEgrams were generated for monkeys and humans from approximately f2 = 0.5-20 kHz. Monkeys had larger amplitude DPOAEs at all frequencies except around f2 = 1 kHz. In the second condition, DPOAE amplitudes increased and then decreased as the separation between the primaries increased. These functions were similar in the two species except at the lowest frequencies assessed. In the third condition, the levels of the primaries were varied independently. Monkeys had steeper input/output (I/O) functions than humans. The slopes of DPOAE I/O functions increased with frequency in both species. When the levels of both primaries were increased simultaneously, DPOAE I/O functions were well described by power functions throughout the intensity range assessed (from threshold to 65 dB SPL). Monkey I/O functions tended to be expansive power functions at all but the lowest frequencies, while human I/O functions tended to be compressive power functions except at the highest frequencies assessed. Other differences in I/O functions f2 = 8 kHz may indicate species specific differences at high (for human) frequencies.
Early (ABRs) and middle (MLRs) surface-recorded auditory evoked potentials were compared in eight adult monkeys (Macaca mulatta) and eight adult humans. Responses whose probable generators were the cochlear nucleus and lateral lemniscus were of shorter latency and larger amplitude in monkeys. Relative to humans, ABR response latencies in monkeys were less affected by stimulus intensity, stimulus rate, and masker level. In contrast, monkey amplitudes were relatively more affected by those same stimulus parameters. The most prominent MLR wave was longer in latency and greater in amplitude in humans than the homologous wave in monkeys. The reduction in amplitude of that wave with increasing rate was greater for humans than monkeys. Temporal interactions (the effect of prior stimuli on the response to current stimulation) were investigated from a non-linear systems identification framework using maximum length sequences (MLSs). Both monkey and human auditory systems were second and probably third-order systems at the levels assessed. As the separations between the stimulus pulses decreased, evidence for temporal interactions became more prominent, reached a maximum, and then decreased with further decreases in stimulus pulse separation. At the highest stimulus rates presented, variations in temporal spacing among stimuli had less of an effect on monkey than human evoked responses.
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Exposure to lead in the workplace or home environment has been implicated as a cause of decreased fertility in women. In a previous study, as part of our effort to determine effects of lead in primates, female rhesus monkeys were exposed to lead acetate in drinking water (n = 10) or provided water with no added lead (n = 7) for 33 mo. Lead was administered at levels between 2 and 8 mg/kg/day, with doses adjusted to keep blood lead values near a target of 70 micrograms/dl (observed mean +/- SEM = 68.9 +/- 6.54 micrograms/dl). Blood lead concentrations in control animals were less than 10 micrograms/dl. No significant differences were detected between control and experimental animals in body weight, hematocrit, or general health. Female monkeys receiving lead exhibited longer and more variable menstrual cycles and shorter menstrual flow. In the present study, circulating amounts of progesterone (P4) were determined to evaluate luteal function during the final 7 mo of treatment with lead. Several characteristics were altered as a result of lead treatment: circulating amounts of P4 were reduced as indicated by relative units of area under the concentration-time curve, maximal amounts of P4 were reduced, and P4 levels were greater than 1 ng/ml on fewer days. There were no significant differences between groups in mean percent of anovulatory cycles. Therefore, although chronic treatment with the levels of lead used in this study did not prevent ovulation, luteal function was suppressed. These results extend previous observations of adverse effects of lead on ovarian activity and fertility in monkeys.
Categorical perception of voicing contrasts was evaluated in rhesus monkeys. The monkeys had been chronically exposed to subclinical levels of lead either from conception to birth, or for approximately 6 months postnatally beginning at birth, or were never exposed to lead. Auditory evoked responses were recorded at 1 year of age from scalp electrodes placed over the left and right hemispheres during stimulus presentation. A late component of the brain responses recorded from the right temporal region of all monkeys discriminated between stimuli in a categorical manner. This pattern of responses was noted to be similar to that previously reported for humans. Categorical discriminations were also noted earlier in the waveforms for control monkeys and for monkeys exposed to lead prenatally, although this discrimination pattern shifted to the left hemisphere of the latter group. No such effects were noted for monkeys exposed to lead postnatally. These results suggest that the neurocortical mechanisms associated with categorical perception for voicing information may be similar across human and nonhuman primates. However, early exposure to lead appears to alter these processes.
Adult, female rhesus monkeys ingested lead daily for three 1-year exposures over a 5-year period followed by chronic lead intake for 3 additional, consecutive years. Lead was administered as lead acetate in the drinking water at levels producing average circulating concentrations of lead between 44 and 89 micrograms/100 ml and zinc protoporphyrin concentrations between 87 and 105 micrograms/100 ml. The monkeys were without overt signs of lead toxicity at all times; i.e., appetite, body weight, and hematocrit levels were normal. Menstrual cycles were altered by lead. During the last 2 years of exposure, the lead-treated monkeys had less frequent cycles, longer and more variable intercycle intervals, and fewer days of vaginal bleeding than controls. These differences were not due to seasonal artifacts or differences in exposure to environmental influences such as light or diet. Further, historical data indicated that cycles were normal for the treated monkeys prior to exposure to lead and that three of four cycle characteristics remained normal during the first lead exposures. Duration of vaginal bleeding was initially attenuated by lead but returned to normal when lead intake was discontinued between exposures. In contrast, the effects of lead observed during the later years of exposure remained apparent 1 year following termination of lead ingestion. These results suggest that persistent alterations of the menstrual cycle and perhaps premature menopause resulted from prolonged exposure to lead at levels which produced no obvious signs or symptoms of toxicosis.
Categorical perception of place of articulation contrasts was evaluated in rhesus monkeys. The monkeys had been chronically exposed to subclinical levels of lead, either from conception to birth, or for approximately 6 months beginning at birth, or were never exposed to lead. Auditory evoked responses were recorded from scalp electrodes placed over left and right hemispheres during stimulus presentation. The brain responses recorded from the right hemisphere of the normal control group of monkeys discriminated between the categories of [dae] and [gae]. Categorical discriminations were also noted for monkeys exposed to lead either prenatally or postnatally. These discriminations, in contrast, were found over only the left hemisphere. In additions, postnatal exposure resulted in categorical discrimination associated with slower latency components, suggesting a less mature pattern than that obtained for prenatally exposed monkeys. Finally, the brain responses of the animals in the normal control and postnatal exposure conditions evidenced reliable within-category, as well as between-category, discriminations. These results suggest that the neurocortical mechanisms associated with categorical perception of place information may differ between human and nonhuman primates and that early exposure to lead alters these processes.