BackgroundUrinary mercury concentrations are widely used as a measure of mercury exposure from dental amalgam fillings. No studies have evaluated the relationship of these measures in a longitudinal context in children.ObjectiveWe evaluated urinary mercury in children 8–18 years of age in relation to number of amalgam surfaces and time since placement over a 7-year course of amalgam treatment.MethodsFive hundred seven children, 8–10 years of age at baseline, participated in a clinical trial to evaluate the neurobehavioral effects of dental amalgam in children. Subjects were randomized to either dental amalgam or resin composite treatments. Urinary mercury and creatinine concentrations were measured at baseline and annually on all participants.ResultsTreatment groups were comparable in baseline urinary mercury concentration (~ 1.5 μg/L). Mean urinary mercury concentrations in the amalgam group increased to a peak of ~ 3.2 μg/L at year 2 and then declined to baseline levels by year 7 of follow-up. There was a strong, positive association between urinary mercury and both number of amalgam surfaces and time since placement. Girls had significantly higher mean urinary mercury concentrations than boys throughout the course of amalgam treatment. There were no differences by race in urinary mercury concentration associated with amalgam exposure.ConclusionsUrinary mercury concentrations are highly correlated with both number of amalgam fillings and time since placement in children. Girls excrete significantly higher concentrations of mercury in the urine than boys with comparable treatment, suggesting possible sex-related differences in mercury handling and susceptibility to mercury toxicity.
Methylmercury, a potent neurotoxicant, accumulates in the brain as well as the kidney during chronic exposure. We evaluated the capacity of 2,3-dimercapto-1-propanesulfonic acid (DMPS), a tissue-permeable metal chelator, to reduce brain, kidney, and blood Hg levels and to promote Hg elimination in urine following exposure of F-344 rats to methylmercury hydroxide (MMH) (10 ppm) in drinking water for up to 9 weeks. Inorganic (Hg2+) and organic (CH3Hg+) mercury species in urine and tissues were assayed by cold vapor atomic fluorescence spectroscopy (CVAFS). Following MMH treatment for 9 weeks, Hg2+ and CH3Hg+ concentrations were 0.28 and 4.80 microg/g in the brain and 51.5 and 42.2 microg/g in the kidney, respectively. Twenty-four hours after ip administration of a single DMPS injection (100 mg/kg), kidney Hg2+ and CH3Hg+ declined 38% and 59%, whereas brain mercury levels were slightly increased, attributable entirely to the CH3Hg+ fraction. Concomitantly, Hg2+ and CH3Hg+ in urine increased by 7.2- and 28.3-fold, respectively, compared with prechelation values. A higher dose of DMPS (200 mg/kg) was no more effective than 100 mg/kg in promoting mercury excretion. In contrast, consecutive DMPS injections (100 mg/kg) given at 72-h intervals significantly decreased total mercury concentrations in kidney, brain, and blood. However, the decrease in brain and blood mercury content was restricted entirely to the CH3Hg+ fraction, consistent with the slow dealkylation rate of MMH in these tissues. Mass balance calculations showed that the total amount of mercury excreted in the urine following successive DMPS injections corresponds quantitatively to the total amount of mercury removed from the kidney, brain, and blood of MMH-exposed rats. These findings confirm the efficacy of consecutive DMPS treatments in decreasing mercury concentrations in target tissue and in reducing overall mercury body burden. They demonstrate further that the capacity of DMPS to deplete tissue Hg2+ is highly tissue-specific and reflects the relative capacity of the tissue for methylmercury dealkylation. In light of this observation, the inability of DMPS to reduce Hg2+ levels in brain or blood may explain the inefficacy of DMPS and similar chelating agents in the remediation of neurotoxicity associated with prolonged MMH exposure.
Changes in urinary porphyrin excretion patterns (porphyrin profiles) during prolonged mercury exposure are attributable to mercury accumulation in the kidney and to consequent effects of Hg2+ on renal porphyrin metabolism. In the present study, we evaluated the quantitative relationship of urinary porphyrin concentrations to mobilizable renal mercury content, using the metal chelator 2,3-dimercapto-1-propanesulfonic acid (DMPS) to modulate kidney mercury levels. Rats exposed to methylmercury hydroxide (MMH) at 10 ppm in drinking water for 6 weeks were treated with up to 3 consecutive doses of DMPS (100mg/kg, ip) at 72-h intervals. Consistent with previous findings, the concentrations of pentacarboxyl- (5-) and copro- (4-) porphyrins and of an atypical porphyrin specific to mercury exposure, precoproporphyrin, were significantly elevated in urine of MMH-exposed rats, compared with that of rats exposed to distilled water (dH2O) for the same period. Consecutive DMPS treatments of MMH-exposed rats significantly decreased kidney concentrations of total, as well as Hg2+ and CH3Hg+ species, and promoted increased urinary mercury excretion. Concomitantly, DMPS treatment decreased both kidney and urinary porphyrin concentrations, consistent with depletion of renal mercury levels. Regression analyses demonstrated a high correlation (r approximately 0.9) between prechelation urinary porphyrins and postchelation urinary mercury levels and also between prechelation urinary porphyrins and prechelation kidney mercury concentrations. These findings demonstrate that urinary porphyrin concentrations relate quantitatively to DMPS-mobilizable mercury in the kidney and, therefore, serve as a biochemical measure of renal mercury content.
Nuclear factor kappa B (NF-kappaB), a pleiotropic transcriptional factor that promotes cell survival and protects cells from apoptosis, requires reduced thiols at critical steps in its activation pathway. Mercuric ion (Hg(2+)), one of the strongest thiol-binding agents known, impairs NF-kappaB activation and transcriptional activity in normal rat kidney epithelial (NRK52E) cells at concentrations as low as 0.5 microM by binding to specific reduced thiol moieties in the NF-kappaB activation pathway. We hypothesized that prevention of NF-kappaB activation by Hg(2+) will increase the sensitivity of kidney cells to the apoptosis-inducing effects of other toxicants to which these cells are otherwise resistant by virtue of their NF-kappaB-activating capacity. Fewer than 5% of untreated kidney cells in culture (70-90% confluent) were found to be apoptotic when evaluated by DNA fragmentation (terminal deoxynucleotide transferase-mediated dUTP nick-end labeling) or flow cytometric DNA profile analyses. Hg(2+) (5 microM) treatment for 24 hr increased this proportion by 1.5- to 2-fold. Neither lipopolysaccharide (LPS) (1 microg/mL) nor tumor necrosis factor-alpha (TNF-alpha; 300 U/mL), both potent activators of NF-kappaB in kidney cells, significantly altered the proportion of apoptotic cells, compared with untreated controls, when applied without Hg(2+) pretreatment. However, when LPS or TNF-alpha was administered after Hg(2+) pretreatment (5 microM for 30 min), the proportion of cells undergoing apoptosis 22 hr later increased by 4- to 6-fold compared with untreated controls. In contrast, Hg(2+) pretreatment did not increase the amount of apoptosis caused by apoptosis-inducing agents that do not activate NF-kappaB (staurosporine, Fas ligand). These findings suggest that Hg(2+) enhances the sensitivity of kidney cells to apoptotic stimuli as a consequence of inhibition of NF-kappaB activity. Because apoptosis is known to play a key role in the pathogenesis of renal failure resulting from toxicant injury to proximal tubular cells, promotion of apoptosis via inhibition of NF-kappaB activity may define a novel molecular mechanism by which Hg(2+) toxicity is initiated in kidney cells.
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