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The industrial revolution
and its resultant technological society have led to the redistribution
of compounds toxic to organisms and to the synthesis of substances
previously unknown to nature. The result of these events has been
a gradual, diffuse contamination of the entire planet. No region
on Earth remains as clean as it did before these events. This unprecedented
phenomenon is often referred to as the toxification of nature. For
the first time in history, all of the Earth’s organisms are
being subjected to complex mixtures of toxic substances, albeit at
low-doses. The bioaccumulation and degradation of toxic compounds
are highly dependent on temperature and radiation. Redistribution
occurs primarily via the atmosphere. Climate change factors such
as increases in temperature, and fluctuations in rainfall, cloud
cover, windfall or distribution of dust, can also affect the mobility
of pollutants. These processes are particularly important for contaminants
that are transported over large distances by the atmosphere and subsequently
enter the water cycle. This is especially true for hydrophobic contaminants
that accumulate in soil and organisms. Water quality can therefore
be compromised by the build up of pollutants during water storage
and transport, and is thereby subject to the effects of climate change.
Metals, namely mercury, and persistent organic pollutants (POPs)
are the toxic products for which environmental distribution is most
influenced by climate. POPs were the subject of the Stockholm convention
(22-23 May 2001), whereby member states agreed to reduce or eliminate
their use and emission as well as promote research on their impact
in the environment and human health. These compounds are known mutagens,
carcinogens and teratogens, and are classified as 2A or 2B by the
IARC (IARC, 1983). Natural distillation and condensation of POPs
coupled with atmospheric transport have led to their accumulation
in high-altitude ecosystems and organisms (Wania and Mackay, 1993).
In the near future, the deposition patterns of POPs will most likely
be under the influence of climate change as their retention in freshwater
accumulation zones following atmospheric transport depends on local
temperature (Carrera et al., 2002; Grimalt et al., 2001). Higher
temperatures will cause greater emissions, as well as further melting
of mountain ice, which will in turn increase the amount of pollutants
leaked into water used for human consumption.
Carrera, G., P. Fernández,
R.M. Vilanova and J.O. Grimalt (2001) Persistent organic pollutants
in snow from European high mountain areas. Atmos. Environ. 35, 245-254. |
Grimalt, J.O., P. Fernandez, L. Berdié,
R.M. Vilanova, J. Catalan, R. Psenner, R. Hofer, P.G. Appleby, B.O. Rosseland,
L. Lien, J.C. Massabuau and R.W. Battarbee (2001) Selective trapping of
organochlorine compounds in mountain lakes of temperate areas. Environmental
Science and Technology 35, 2690-2697. |
International Agency for Research on Cancer. Some
drinking water disinfectants and contaminants, including arsenic. IARC
Scientific Publications (2002). |
Wania, F. and D. Mackay (1993). Global fractionation
and cold condensation of low volatility organochlorine compounds in polar
regions. Ambio 22, 10-18. |
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