Blood mercury in workers exposed to the preparation of mercury cadmium telluride layers on cadmium telluride base.
(73/76)
Study was conducted in a group of 32 persons engaged in liquid phase epitaxial growth of mercury cadmium telluride (MCT) layers for nearly 11 years. Airborne mercury concentrations in work environment have been exceeding the threshold limit value of 0.05 mg/m3 recommended by ACGIHD. Hg concentration in workplace during peak working hours remained between 0.04-0.08 mg/m3. Findings were compared with 32 unexposed referents. Mercury value was estimated 1.60 +/- 0.20 (mean +/- SD) in control, and in Phase I and II, 10.72 +/- 1.34 ng Hg/ml and 8.08 +/- 1.15 ng Hg/ml of blood respectively. Results indicate a fall in blood mercury level during the second phase of study. But the values did not return to normal even after a gap of 3 months. An individual who met with a mercury accident showed 226 ng Hg/ml of blood which decreased to 25 ng/ml after 3 months. It is inferred from the present study that Hg level has increased significantly in MCT workers during working period, and also in non-working period, the values were higher than controls. (+info)
Historical exposure to inorganic mercury at the smelter works of Abbadia San Salvatore, Italy.
(74/76)
Metallic mercury production from cinnabar ore may result in high exposures to inorganic mercury, that are difficult to assess separately from the exposures originating from underground extraction, and previously have only been scantily described. We retrieved and analysed the air and biological mercury determinations on workers involved in the smelting process of the Abbadia San Salvatore mine (Monte Amiata, Italy). Native mercury was not present in the ore, and the exposure in the underground extraction was low. The smelter operated from 1897 to 1983. Blood and urine (24/h urine collections and concentration samples) had been sampled in 1968 to 1982, and analysed for mercury by atomic absorption spectrophotometry, and relate to all subjects. Exposure to mercury in air had been determined in a small set of personal samples in 1982. The data relate to all jobs in the smelter process, and all jobs entailed substantial exposure to mercury. The overall distribution of breathing zone air, blood and urinary levels is right-skewed and similar to the log-normal distribution (air, median 48 micrograms/m3, n = 49; blood, arithmetic mean AM 49 micrograms/L; geometric mean GM 26 micrograms/L, n = 192; urinary excretion, AM 140 micrograms/24 h, GM 78 micrograms/24 h, n = 839; and urinary concentration, AM 160 micrograms/L, GM 83 micrograms/L, n = 632). Air, blood and urinary values show a high ratio of the between- and within-job variance, indicating differences in exposure by job. Cinnabar pigment production, of which the exposure has not been characterised previously, was the job with the highest air (AM 160 micrograms/m3) and urinary levels (excretion AM 690 micrograms/24 h; concentration AM 1100 micrograms/L). Other jobs with high urinary levels were soot purification, laboratory work, and bottling. Cleaning of condensers showed the highest blood level (AM 280 micrograms/L). There is a downwards time trend in mercury concentration in blood and in urine. The corresponding trend is not seen for urinary excretion levels, the reason for this being unclear. Roasters, which is the most frequently monitored group, show however a decreasing trend in all sets of data (e.g. the mean of urinary excretion decreased from 300 micrograms/24 h in 1968/69 to 50 micrograms/24 h in 1980/81). The mercury exposure experienced by the smelters of Abbadia San Salvatore is in line with the few available data on workers from other mercury mines and smelters, and our data confirm the high exposure levels in this occupational group, in particular at cinnabar pigment production, soot purification, and condenser cleaning. (+info)
DMPS (2,3-dimercaptopropane-1-sulfonate, dimaval) decreases the body burden of mercury in humans exposed to mercurous chloride.
(75/76)
DMPS (2,3-dimercaptopropane-1-sulfonate, Na salt), when used as a challenge test for mercury in workers involved in the production of a calomel skin-bleaching lotion and in direct contact with mercurous chloride, elevated urine levels of mercury. A DMPS treatment regimen was devised and initiated. Three days after the challenge test, DMPS was administered p.o. (400 mg per day) for 8 days, followed by a no-treatment period of five days. A new cycle of DMPS treatment for 7 days was initiated and followed by 5 days without treatment. A third period of treatment was begun for 6 days, followed by a 5-day no-treatment period. The urinary mercury greatly increased during those periods when DMPS was administered (1754, 314, and 173 microgram/24 h for the periods 1, 2 and 3, compared with 106, 48 and 53 microgram/24 h on the corresponding no-treatment periods). One of the workers presented signs of drug intolerance and was discharged after receiving the first cycle of treatment. DMPS treatment was effective in lowering the body burden of mercury and in decreasing the urinary mercury concentration to normal levels. (+info)
Binding sites for the (Hg-Se) complex on selenoprotein P.
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The mechanism underlying the interaction between mercury (Hg), selenium (Se) and selenoprotein P (Sel P) in the bloodstream has been explained by the formation of the [(Hg-Se)n]m-Sel P complex. In the present study, the binding sites for the (Hg-Se)n complex on Sel P were studied by competitive assay of the binding of the (Hg-Se)n complex to Sel P with polymeric and monomeric amino acids with simultaneous detection of the Hg, Se of selenite origin and Se of Sel P origin by the high performance liquid chromatography-inductively coupled argon plasma-mass spectrometry method. The specific binding of the (Hg-Se) complex but not Hg2+ or selenide to Sel P was explained by the unique binding sites consisting of the cationic and anionic ends such as imidazolyl and selenol groups on Sel P, respectively. The number, n, in the (Hg-Se)n complex was estimated to be approx. 100, while the number, m, in the [(Hg-Se)n]m-Sel P complex was estimated to be 35. The formation of the unit complex (Hg-Se)100, followed by its binding to Sel P at up to the 35 binding sites on Sel P was suggested. (+info)