Biology Reference
In-Depth Information
Different classes
of pollutants
Hydromorphology
Bioavailability
Mixture
Physicochemistry
Ecological
factors
General
conditions
(salinity...)
Population
Organism
Physical medium
Biomarkers
Ecologically relevant
biomarkers
Indirect effect
Defense amage
Direct effect
(reproduction)
(lysosomal stability
behavior, energy,
genotoxicity,
immunotoxicity)
FIGURE 16.1
Methods for quality assessment of aquatic environments.
characterized by important spatiotemporal changes in temperature, pH, dissolved O 2 , redox
potential, hydrodynamics, and sedimentary processes, plus salinity in the case of estuaries.
Bioindicators at supra-individual levels of biological organization are long-term responses
that often appear when the pollution impact has been at work for years (Figure 1.3). This lack
of both specificity and precociousness is a serious restraint to their usefulness for environ-
mental protection even though their use is imposed in regulations such as the WFD.
16.1.3 Biomarkers
In contrast to these high-level bioindicators, individual and infra-individual responses
used as biomarkers have attracted considerable interest as they are able to constitute early
and sensitive tools for the assessment of environmental health. The methodology of bio-
markers has given rise to a rocketing number of publications, from about 100 in 1991 to
about 3000 in 2007 (Jemec et al. 2010). These authors have reviewed the criteria for the use
of biomarkers in environmental pollution studies:
• The relationship between the level and the duration of exposure and the bio-
marker response must be established.
• The effect of confounding factors, both intrinsic and extrinsic, must be well under-
stood. Infra-individual biomarkers should be detected at lower concentrations of
exposure than individual responses.
• The changes that occur at a given level of organization must be indicative of
changes at the next level (infra-individual toward individual, individual toward
supra-individual).
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