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NANOMEDICINE - Toxicity under nano-surveillance
The ‘nano’ prefix can cause confusion, insofar as it can relate to the dimension in which a new kind of scientific activity is conducted (nanotechnologies) or the depth of analysis of a phenomenon being studied. Thus, when one speaks of research on the toxicity of nanoparticles, the reference is not to a danger posed by nanotechnologies specifically – although this could be the case – but to the mechanisms at work when one analyses the specific toxic effects of all kinds of particles (of anthropic as well as natural origin) on the nano scale. This is a new field and it is only now being explored.
The first is awareness of the dangers of transport-related pollution which, according to the WHO, results in 80 000 premature deaths a year in Europe. It is now clear that the pollutants that are usually studied (ozone, nitrogen or sulphur monoxide, etc.) do not in themselves explain this mortality, and that small suspended particles, known as PM10s (1), which are released by diesel engines in particular, also play a role. The second relates to what was a huge failure on the part of toxicologists in being unable to warn of the health risks of asbestos, as a result of which tens of thousands of people suffered. In this latter case too, it is minute suspended particles, just a few micrometres in length, which are responsible for the damage. The smaller the particles the easier it is for them to penetrate the respiratory system. So, if microparticles such as those linked to air or asbestos pollution present such serious risks to health, there would seem to be good reason to be suspicious of particles that are a thousand times smaller. Risk = danger x exposure Toxicologists are not starting from scratch in their exploration of the toxicity of nanoparticles. They already have a conceptual framework summed up by the equation: risk = danger x exposure. The danger is an intrinsic characteristic of a substance, while the exposure varies depending on behaviour. As Ken Donaldsen explains, “the danger of using a chainsaw is of cutting oneself, but the risk is very different depending on whether it is used by a forester wearing all the protective gear or in a juggling act!”. In practice, it is difficult to quantify these two elements. The danger depends on the nature of the nanoparticle, its size and active surface area, the individual who absorbs it, the organ studied, and often varies depending on whether the exposure is isolated or regular. As to the exposure, that is a factor that has to be reconstructed after the event with all the unknowns that this implies. Effective toxicity
As a result of this inability to evaluate the danger we are unable to estimate the exposure. The latter must be expressed in a unit of measurement that reflects what the specialists call the ‘toxicity effect’, that is, the principal component of the toxicity. For the PM10s, this is the mass and they are therefore quantified in micrograms/ m3; for asbestos, it is the fibres, and the unit of measurement is the number of fibres per m3. And for nanoparticles? It is impossible to say at present. The only point on which researchers agree is that their surface area must be taken into account. For geometric reasons, 1 000 particles of 100 nanometres in diameter have a bigger surface area than a single particle measuring 1 micrometre in diameter, hence an increase in the possibilities for contact with biological tissue. There is therefore an urgent need to reach a consensus on the unit of measurement because, as Rob Aitken of Edinburgh University’s Institute of Occupational Medicine points out, “the rare data we have at present for measuring the toxicity of nanoparticles cannot be compared the one with the other as they are not expressed in the same units”. Ingesting, touching, inhaling To be able to determine the two key variables of nanoparticles – danger and exposure – toxicologists therefore have no alternative but to return to physiology to determine the path they take in the body. Theoretically, there are three possible means of access to the body’s interior and its vital organs: by means of ingestion, through the intestinal mucosa; by means of simple contact, through the skin; or by means of inhalation, with subsequent transport through the blood, through the pulmonary alveoli, or directly into the brain through the neurones and olfactive mucosa. It is only the latter of these three means of penetration that has so far been confirmed. As Günter Oberdörster, of Rochester University (United States), a pioneer in this field points out, “we have known since 1914 that when administered to a chimpanzee, a poliomitis virus, which measures no more than 30 nanometres, reaches the brain at a speed of 2.4 millimetres an hour by way of the olfactive neurones”. This observation has been repeated on many occasions, to the point of being used as a method for the study of olfactive neurone connections. Oberdöster’s work has also shown that nanoparticles could follow this path to quickly reach the upper centres of the brain: the cortex, thalamus and cerebellum. What are the consequences of their presence here? “Our preliminary results, among healthy volunteers, show that inhalation of nanoparticles emitted by the diesel engine changes the electroencephalogram rate,” explains Paul Borm of the Centre for Expert Assessment in Life Science in An Herlen (the Netherlands). And in the longer term? “That is one of the questions to be resolved in the coming years, in particular by studying the possibility of neurodegeneration,” admits Günter Oderdöster. Much less is known about the mechanism for absorption by the lungs or intestine. The only certainty here is that exposure to certain nanoparticles can cause cardiac problems in animals. Some believe this is because the cells of the pulmonary epithelium are able to absorb these nanoparticles and transport them to the bloodstream, from where they spread throughout the body and thus also to the heart. Others see it as an indirect effect linked to the inflammation of the pulmonary mucosa through contact with the nanoparticles. Even less is known about possible absorption through the skin. The European NANOderm project was one of the first to tackle this question, through the in vivo and in vitro study, on human and pig skin cultures, of the passage of titanium oxide nanoparticles through the skin. This research is not without its economic significance as these particles are widely used in the cosmetic industry and are present in many sun lotions. After two years of research, Project Coordinator Tilman Butz of Leipzig University (Germany) is reassuring: ”Titanium oxide nanoparticles remain blocked in the upper layers of the epidermis and almost never penetrate to the dermis, except along the follicular cells that generate hairs.” The NANOderm consortium is nevertheless to continue its research to find out if damaged skin (burns, psoriasis, etc.) continues to act as an effective barrier. (1) PM10 refers to the fine suspended dust particles of an aerodynamic diameter of under ten micrometres. Formed of both primary and secondary pollutants, of natural or anthropic origin (soot, geological matter, abrasion dust, biological matter, etc.), this dust has a very variable composition (heavy metals, sulphates, nitrates, ammonium, organic carbon, aromatic polycyclic hydrocarbons, dioxins and furans). |
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