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Robert Lauwerys

Bio: Robert Lauwerys is an academic researcher from Catholic University of Leuven. The author has contributed to research in topics: Population & Cadmium. The author has an hindex of 76, co-authored 379 publications receiving 19347 citations. Previous affiliations of Robert Lauwerys include Université catholique de Louvain.


Papers
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Journal ArticleDOI
TL;DR: The urinary elimination of the metabolites of arsenic has been followed up as a function of time in volunteers who ingested a single oral dose of arsenic either as sodium arsenite (Asi), monomethylarsonate (MMA), or cacodylate (DMA).
Abstract: The urinary elimination of the metabolites of arsenic has been followed up as a function of time in volunteers who ingested a single oral dose of arsenic (500 μg As) either as sodium arsenite (Asi), monomethylarsonate (MMA), or cacodylate (DMA). The excretion rate increased in the order Asi < DMA < MMA. After 4 days, the amount of arsenic excreted in urine represents 46, 78, and 75% of the ingested dose in the case of Asi, MMA and DMA, respectively. With regard to the in vivo biotransformations, it is concluded that DMA is excreted unchanged; MMA is slightly (13%) methylated into DMA while roughly 75% of the arsenic excreted after ingestion of Asi is methylated arsenic (about 1/3 as MMA and about 2/3 as DMA).

519 citations

Journal ArticleDOI
TL;DR: Five variables (urinary excretion of retinol-binding protein, N-acetyl-beta-glucosaminidase, beta 2-microglobulin, aminoacids, and calcium) were significantly associated with the urinaryexcretion of cadmium (as a marker of cad mium body burden), suggesting the presence of tubular dysfunction.

503 citations

Book
01 Jan 1993
TL;DR: Biological Monitoring of Exposure to Industrial Chemicals Classification of Biological Monitoring Methods Principal Advantages and Limitations of biological Monitoring Biological Monitoring of Susceptibility Selection of the Appropriate Biological Media and Sampling Time Interpretation of Results Biological Monitoring for Exposure to Inorganic and Organometallic Substances Aluminum Antimony Arsenic Barium Beryllium Bromine Cadmium Carbon Disulfide Chromium Cobalt Copper Fluoride Germanium Hydrogen Sulfide Lead Manganese Mercury Molybdenum Nickel Nitrous Oxide Perchlorate Platinum Selenium
Abstract: Introduction Definitions and Objectives of Biological Monitoring of Exposure to Industrial Chemicals Classification of Biological Monitoring Methods Principal Advantages of Biological Monitoring Conditions and Limitations of Biological Monitoring Biological Monitoring of Susceptibility Selection of the Appropriate Biological Media and Sampling Time Interpretation of Results Biological Monitoring of Exposure to Inorganic and Organometallic Substances Aluminum Antimony Arsenic Barium Beryllium Bromine Cadmium Carbon Disulfide Chromium Cobalt Copper Fluoride Germanium Hydrogen Sulfide Lead Manganese Mercury Molybdenum Nickel Nitrous Oxide Perchlorate Platinum Selenium Silver Tellurium Thallium Uranium Vanadium Zinc Biological Monitoring of Exposure to Organic Substances Unsubstituted Aliphatic and Alicyclic Hydrocarbons Unsubstituted Aromatic Hydrocarbons Halogenated Hydrocarbons Amino and Nitro Derivatives Alcohols Glycols and Derivatives Ketones Aldehydes Amides and Anhydrides Phenol and Derivatives Carbon Monoxide Cyanides and Nitriles Isocyanates Pesticides Ethers Miscellaneous Chemicals Mutagenic and Carcinogenic Substances Summary of Recommendations

361 citations

Journal ArticleDOI
TL;DR: It can be considered as evident, however, that the ultimate mutagen which binds to the genetic material is the triavalent form produced intracellularly from hexavalent chromium, the apparent lack of activity of the trivalent form being due to its poor cellular uptake.
Abstract: Occupational exposure represents the main source of human contamination by chromium. For non-occupationally exposed people the major environmental exposure to chromium occurs as a consequence of its presence in food. Chromium must be considered as an essential element. Its deficiency impairs glucose metabolism. Trivalent chromium salts are poorly absorbed through the gastro-intestinal and respiratory tracts because they do not cross membranes easily. Hexavalent chromium can be absorbed by the oral and pulmonary routes and probably also through the skin. After its absorption, hexavalent chromium is rapidly reduced to the trivalent form which is probably the only form to be found in biological material. Epidemiological studies have shown that some chromium salts (mainly the slightly soluble hexavalent salts) are carcinogens. Lung cancers have, indeed, often been reported among workers in chromate-producing industry and, to a lesser extent, in workers from the chrome-pigment industry. The first attempts to produce cancers in experimental animals by inhalation or parenteral introduction gave negative or equivocal results but, from 1960, positive results have been obtained with various chromium compounds. As for the carcinogenic activity, the mutagenicity of chromium has mainly been found with hexavalent salts. In the majority of assay systems used, trivalent chromium appears inactive. It can be considered as evident, however, that the ultimate mutagen which binds to the genetic material is the trivalent form produced intracellularly from hexavalent chromium, the apparent lack of activity of the trivalent form being due to its poor cellular uptake.

301 citations


Cited by
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TL;DR: Recent data indicate that adverse health effects of cadmium exposure may occur at lower exposure levels than previously anticipated, primarily in the form of kidney damage but possibly also bone effects and fractures, and measures should be taken to reduce cadmiam exposure in the general population in order to minimize the risk of adverse health results.
Abstract: The main threats to human health from heavy metals are associated with exposure to lead, cadmium, mercury and arsenic. These metals have been extensively studied and their effects on human health regularly reviewed by international bodies such as the WHO. Heavy metals have been used by humans for thousands of years. Although several adverse health effects of heavy metals have been known for a long time, exposure to heavy metals continues, and is even increasing in some parts of the world, in particular in less developed countries, though emissions have declined in most developed countries over the last 100 years. Cadmium compounds are currently mainly used in re-chargeable nickel-cadmium batteries. Cadmium emissions have increased dramatically during the 20th century, one reason being that cadmium-containing products are rarely re-cycled, but often dumped together with household waste. Cigarette smoking is a major source of cadmium exposure. In non-smokers, food is the most important source of cadmium exposure. Recent data indicate that adverse health effects of cadmium exposure may occur at lower exposure levels than previously anticipated, primarily in the form of kidney damage but possibly also bone effects and fractures. Many individuals in Europe already exceed these exposure levels and the margin is very narrow for large groups. Therefore, measures should be taken to reduce cadmium exposure in the general population in order to minimize the risk of adverse health effects. The general population is primarily exposed to mercury via food, fish being a major source of methyl mercury exposure, and dental amalgam. The general population does not face a significant health risk from methyl mercury, although certain groups with high fish consumption may attain blood levels associated with a low risk of neurological damage to adults. Since there is a risk to the fetus in particular, pregnant women should avoid a high intake of certain fish, such as shark, swordfish and tuna; fish (such as pike, walleye and bass) taken from polluted fresh waters should especially be avoided. There has been a debate on the safety of dental amalgams and claims have been made that mercury from amalgam may cause a variety of diseases. However, there are no studies so far that have been able to show any associations between amalgam fillings and ill health. The general population is exposed to lead from air and food in roughly equal proportions. During the last century, lead emissions to ambient air have caused considerable pollution, mainly due to lead emissions from petrol. Children are particularly susceptible to lead exposure due to high gastrointestinal uptake and the permeable blood-brain barrier. Blood levels in children should be reduced below the levels so far considered acceptable, recent data indicating that there may be neurotoxic effects of lead at lower levels of exposure than previously anticipated. Although lead in petrol has dramatically decreased over the last decades, thereby reducing environmental exposure, phasing out any remaining uses of lead additives in motor fuels should be encouraged. The use of lead-based paints should be abandoned, and lead should not be used in food containers. In particular, the public should be aware of glazed food containers, which may leach lead into food. Exposure to arsenic is mainly via intake of food and drinking water, food being the most important source in most populations. Long-term exposure to arsenic in drinking-water is mainly related to increased risks of skin cancer, but also some other cancers, as well as other skin lesions such as hyperkeratosis and pigmentation changes. Occupational exposure to arsenic, primarily by inhalation, is causally associated with lung cancer. Clear exposure-response relationships and high risks have been observed.

5,015 citations

Journal ArticleDOI
16 Aug 2002-Talanta
TL;DR: This review deals with environmental origin, occurrence, episodes, and impact on human health of arsenic, a metalloid occurs naturally, being the 20th most abundant element in the earth's crust.

3,166 citations

Journal ArticleDOI
TL;DR: An overview of redox and non-redox metal-induced formation of free radicals and the role of oxidative stress in toxic action of metals is provided.

2,429 citations

Journal ArticleDOI
Paul Claman1
TL;DR: There is accumulating evidence that workplace exposure to toxic substances contributes to male infertility, and men suffering from infertility problems may do well to look at their occupations, where exposure to certain substances may be a contributory factor.

2,428 citations