I'll probably read relatively quickly, because I must have enough for six or seven minutes.
Nanotechnologies are an emerging field with a potential for enormous economic and social development. The reason is very simple: the unique properties of nanoparticles (NP) should allow products with innovative characteristics to be developed, resulting in a multitude of applications in all fields of human activity.
Already, more than 1,000 products containing NPs are commercially available. They are offered by close to 500 companies located in 24 countries. The development and production of these new products should involve an increasing number of Canadian workers. The people potentially exposed to the highest concentration of nanoparticles can be found in the following three groups: researchers who develop new products; employees in companies that synthesize nanoparticles; and employees in companies that purchase nanoparticles for the purpose of introducing them into their production lines in order to create value-added products.
The IRSST's research work has allowed it to assess the state of current international scientific knowledge in the field of health risks related to nanoparticles in the workplace.
First, the concept of risk, i.e., toxic risk, has to be well understood. Toxic risk is the product of two components. The first component, toxicity, is a function of the nature of the product and the characteristics of the substance. The second component is related to the worker's level of absorption of this substance, which is directly linked to the level of air contamination and the worker's exposure time. Consequently, the toxic risk, or health risk, is the product of the toxicity (hazard) and the level of exposure. That can be summed up in a simple equation that clearly shows that, even in the presence of a potentially toxic product, the risk will be minimal if there is no worker exposure.
What do we know about the toxicity of nanoparticles? It is important to mention first that toxicological studies aiming to establish whether nanoparticles demonstrate some toxicity cover only a small proportion of existing nanoparticles. Second, for those that are documented, knowledge is generally insufficient to be able to accurately quantify the hazard. NPs that are insoluble or not very soluble in biological fluids are of the most concern because they can remain in the body for a long time, whereas the toxicity of soluble nanoparticles will mainly be a function of their chemical composition, not their size.
Nevertheless, currently available data show a behaviour that is often unique to NPs. At equal mass, several nanoparticles demonstrate a higher toxicity than the same chemical product of larger size. The measured toxic effects are poorly correlated with the mass. They are better correlated with different parameters, namely the number of particles, size, surface area and some surface properties. Several factors seem to contribute to the toxicity of these new-generation products. Given our fragmentary knowledge, it is currently impossible to weight their respective importance or to accurately predict the toxicity of a new NP.
The behaviour of nanoparticles in the body can be different from that of larger-size particles. In the pulmonary alveoli, our defence mechanisms are less efficient in eliminating nanoparticles than larger size particles. Some NPs can overcome our different defence mechanisms in the lungs, gastro intestinal tract or skin, enter the blood in solid form and from there travel through the body and accumulate at specific sites (liver, kidneys, etc.). Others can travel along the olfactory nerves and enter the brain directly, or even cross cell barriers and reach the cell nucleus.
In animals, a number of studies have demonstrated toxic effects in several organs, including the heart, lungs, kidneys and reproductive system. For example, some particles cause granuloma, fibrosis and tumour reactions in the lungs. Very little is known about the long-term effects of nanoparticles. In most cases, it will be difficult to quantify the specific toxicity of the nanoparticle to which workers are exposed.
The second risk component is related to the worker's exposure, namely to the contamination of the air that he or she breathes. There are numerous instruments for determining certain workplace exposure parameters, such as mass, dimension, number of particles and specific surface. However, few data exist on workplace exposure levels, and research in this field is just beginning to produce its first results.
Nevertheless, two important observations are emerging: the total lack of information on the level of exposure in the great majority of workplaces; and the lack of consensus within the scientific community about the parameters to measure that are representative and that link the exposure level to the product's toxicity.