Mercury

Contact dermatitis in Korean dental technicians.

“The high risk of occupational contact dermatitis in dental personnel are well accepted throughout the world. There are few reports concerning occupational skin disease in dental personnel in Korea. The purposes of this study were to investigate the frequency, characteristics and causative factors of contact dermatitis in Korean dental technicians. Recording of personal history, physical examination and patch tests with the Korean standard series and dental screening series were performed in 49 dental technicians. Most of the subjects were exposed to a variety of compounds, including acrylics, metals, plaster, alginate, etc. 22 (44.9%) subjects had contact dermatitis, present or past, and the site involved was the hand in all 22. The most common clinical feature of hand dermatitis was itching (77.3%); scaling, fissuring and erythema were other common clinical features. Metals, including potassium dichromate (24.5%), nickel sulfate (18.4%), mercury ammonium chloride (16.3%), cobalt chloride (12.2%) and palladium chloride (10.2%), showed high positive rates in patch test results of 49 dental technicians. 7 positive reactions to the various acrylics were found in 3 subjects. In our study, the frequency and clinical features of the contact dermatitis showed a similarity to other reports, though the patch test results were somewhat different; a higher patch-positive reaction to metals and a relatively lower patch-positive reaction to acrylics than the patch test results reported in Europe.”

By |2018-06-25T22:06:29+00:00January 1st, 2001|Mercury|

Adverse health effects related to mercury exposure from dental amalgam fillings: toxicological or psychological causes?

“BACKGROUND:

Possible adverse health effects due to mercury released by amalgam fillings have been discussed in several studies of patients who attribute various symptoms to the effects of amalgam fillings. No systematic relation of specific symptoms to increased mercury levels could be established in any of these studies. Thus, a psychosomatic aetiology of the complaints should be considered and psychological factors contributing to their aetiology should be identified.

METHODS:

A screening questionnaire was used to identify subjects who were convinced that their health had already been affected seriously by their amalgam fillings (N = 40). These amalgam sensitive subjects were compared to amalgam non-sensitive subjects (N = 43). All participants were subjected to dental, general health, toxicological and psychological examinations.

RESULTS:

The two groups did not differ with respect to the number of amalgam fillings, amalgam surfaces or mercury levels assessed in blood, urine or saliva. However, amalgam sensitive subjects had significantly higher symptom scores both in a screening instrument for medically unexplained somatic symptoms (SOMS) and in the SCL-90-R Somatization scale. Additionally, more subjects from this group (50% versus 4.7%) had severe somatization syndromes. With respect to psychological risk factors, amalgam sensitive subjects had a self-concept of being weak and unable to tolerate stress, more cognitions of environmental threat, and increased habitual anxiety. These psychological factors were significantly correlated with the number and intensity of the reported somatic symptoms.

CONCLUSIONS:

While our results do not support an organic explanation of the reported symptoms, they are well in accord with the notion of a psychological aetiology of the reported symptoms and complaints. The findings suggest that self-diagnosed ‘amalgam illness’ is a label for a general tendency toward somatization.”

Urinary mercury excretion following amalgam filling in children.

“OBJECTIVES:

Dental amalgam is the major source of inorganic mercury exposure in the general population. Dental amalgam contains approximately 50% mercury, which is a toxic element. Since children are more at risk for mercury toxicity, we aimed to study prospectively the effects of amalgam filling on urinary mercury excretion in 5- to 7-year-old children.

METHODS:

Children admitted to the Pedodontics Department with no previous amalgam filling, and in a good state of health with one or more carious posterior teeth, were selected. All fillings were placed in one session for each child using Sina (Iran) amalgam powder and Degussa (Germany) mercury, which were mixed by an automated electric amalgamator (Dentomate 3, Germany). Urinary mercury concentrations were estimated before and 9-12 days after amalgam filling by atomic absorption using the mercuric hydride system.

RESULTS:

Forty-three children (20 male, 23 female) aged 5.95+/-0.92 years and weighing 19.09+/-3.10 kg were studied. Urinary mercury concentrations before and after amalgam filling were 3.83+/-2.45 and 5.14+/-3.14 microg/L, respectively (p = 0.001). There were no statistically significant correlations between the urinary mercury concentrations and any other variables, including the number and surfaces of filled teeth, weight, age, and sex.

CONCLUSION:

Although there were highly significant increases in urinary mercury concentrations after amalgam filling, no significant correlation was found between the urinary mercury concentration and the amounts of filled amalgam. Additional investigation is required concerning the effects of mercury release from amalgam.”

By |2018-06-25T18:32:01+00:00January 1st, 2001|Mercury|

Mercury toxicity and systemic elimination agents

This paper reviews the published evidence supporting amalgam toxicity and clinical techniques that facilitate mercury elimination. A literature review is provided which documents effective mercury elimination strategies to improve mercury toxicity syndromes. Considering the weight of evidence supporting mercury toxicity, it would seem prudent to select alternative dental restoration materials and consider effective mercury elimination strategies if mercury toxicity is present.

By |2019-05-30T21:25:51+00:00January 1st, 2001|Mercury|

Potential health and environmental issues of mercury-contaminated amalgamators.

BACKGROUND:

Dental amalgamators may become contaminated internally with metallic mercury. This contamination may result from mercury leakage from capsules during trituration or from the long-term accrual from microscopic exterior contaminants that result from the industrial assembly process. The potential health risk to dental personnel from this contamination is unknown.

METHODS:

The authors assessed used amalgamators from the federal service inventory for the amounts of mercury vapor levels, as well as the visual presence of mercury contamination. They evaluated these amalgamators for potential mercury vapor health risk, using established National Institute for Occupational Safety and Health methods and American Conference of Governmental Industrial Hygienists standards.

RESULTS:

Ten of the 11 amalgamators assessed had measurable mercury vapor levels. Four amalgamators were found to have internal static mercury vapor levels above Occupational Safety and Health Administration ceiling limit thresholds. During a simulated worst-case clinical use protocol, the authors found that no amalgamators produced mercury vapor in the breathing space of dental personnel that exceeded established time-weighted federal mercury vapor limits.

CONCLUSIONS:

Amalgamators may be contaminated internally with metallic mercury. Although the authors detected mercury vapor from these units during aggressive, simulated clinical use, dilution factors combined with room air exchange were found to keep health risks below established federal safety thresholds.
CLINICAL IMPLICATIONS:

Dental personnel should be aware that amalgamators may be contaminated with mercury and produce minute amounts of mercury vapor. These contaminated amalgamators may require disposal as environmentally hazardous waste.”

By |2018-07-05T18:59:52+00:00January 1st, 2001|Mercury|

Xenobiotic acceleration of idiopathic systemic autoimmunity in lupus-prone bxsb mice.

“The diverse genetic backgrounds of lupus-prone murine models, which produce both quantitative and qualitative differences in disease expression, may be a valuable resource for studying the influence of environmental exposure on autoimmune disease in sensitive populations. We tested this premise by exposing autoimmune-prone BXSB and the nonautoimmune C57BL/6 mice to the heavy metal mercury. Although both strains express a nonsusceptible H-2 haplotype, exposure to mercury accelerated systemic autoimmunity in both male and female BXSB mice, whereas the C57BL/6 mice were resistant. The subclasses of antichromatin antibodies elicited in BXSB mice by mercury exposure were more consistent with the predominant Th1-type response of idiopathic disease than with the Th2-type response found in mercury-induced autoimmunity (HgIA). The appearance and magnitude of both humoral and cellular features of systemic autoimmunity correlated with the mercury dose. Furthermore, environmentally relevant tissue levels of mercury were associated with exacerbated systemic autoimmunity. These studies demonstrate that xenobiotic exposure can accelerate spontaneous systemic autoimmunity, and they support the possibility that low-level xenobiotic exposure enhances susceptibility to systemic autoimmunity in genetically susceptible individuals.”

Inhibition of the human erythrocytic glutathione-S-transferase T1 (GST T1) by thimerosal.

“We have investigated the interaction of thimerosal, a widely used antiseptic and preservative, with the human erythrocytic GST T1 (glutathione-S-transferase T1). This detoxifying enzyme is expressed in the erythrocytes of solely the human species and it displays a genetic polymorphism. Due to this polymorphism about 25% of the individuals of the caucasian population lack this activity (“non-conjugators”), while 75% show it (“conjugators”) (Hallier, E., et al., 1993). Using our newly developed HPLC-fluorescence detection assay (Müller, M., et al., 2001) we have profiled the kinetics of enzyme inhibition in erythrocyte lysates of two individuals previously identified as “normal conjugator” (medium enzyme activity) and “super-conjugator” (very high activity). For the normal conjugator we have determined a 2.77 mM thimerosal concentration to inhibit 50% of the GST T1 activity. In the case of the super-conjugator a 2.3 mM thimerosal concentration causes a 50% inhibition of the enzyme activity. For both phenotypes a 14.8 mM thimerosal concentration results in residual enzyme activities equal to those typically detected in non-conjugator lysates. Thus, sufficiently high doses of thimerosal may be able to change the phenotypic status of an individual–at least in vitro–by inhibition of the GST T1 enzyme.”

By |2018-06-28T19:28:37+00:00January 1st, 2001|Mercury|
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