Kalina M. Manoylov, Sara Gonçalves, Soizic Morin, Sandra Kim Tiam, David Heudre, Maria Kahlert, Paul B. Hamilton, Mila Kojadinovic-Sirinelli, Lalit K. Pandey, Elisa Falasco, Jonathan C. Taylor, Brigitte Gontero, Claude Fortin, Isabelle Lavoie, Centre Eau Terre Environnement - INRS (INRS-ETE), Institut National de la Recherche Scientifique [Québec] (INRS), University of Toronto, Ecosystèmes aquatiques et changements globaux (UR EABX), Institut national de recherche en sciences et technologies pour l'environnement et l'agriculture (IRSTEA), IRSTEA Bordeaux, Swedish University of Agricultural Sciences (SLU), Dipartimento di Scienze della Vita e Biologia dei Sistemi, Università degli studi di Torino (UNITO), Bioénergétique et Ingénierie des Protéines (BIP ), Aix Marseille Université (AMU)-Centre National de la Recherche Scientifique (CNRS), DREAL Alsace, Incheon National University, South African Institute for Aquatic Biodiversity (SAIAB), South African Institute for Aquatic Biodiversity, Centre Eau Terre Environnement [Québec] (INRS - ETE), INRS EAU QUEBEC CAN, Partenaires IRSTEA, Institut national de recherche en sciences et technologies pour l'environnement et l'agriculture (IRSTEA)-Institut national de recherche en sciences et technologies pour l'environnement et l'agriculture (IRSTEA), CANADIA MUSEUM OF NATURE CAN, Muséum national d'Histoire naturelle (MNHN), UNIVERSITA DEGLI STUDI DI TORINO ITA, Aix Marseille Université (AMU), DREAL GRAND EST STRASBOURG FRA, GEORGIA COLLEGE AND STATE UNIVERSITY MILLEDGEVILLE USA, INCHEON NATIONAL UNIVERSITY INCHEON KOR, NORTH WEST UNIVERSITY POTCHEFSTROOM ZAF, SOUTH AFRICAN INSTITUTE FOR AQUATIC BIODIVERSITY GRAHAMSTOWN ZAFic Biodiversity, Grahamstown South-Africa, Università degli studi di Torino = University of Turin (UNITO), and National Research Foundation [South Africa] (NRF)
International audience; Contaminant-related stress on aquatic biota is difficult to assess when lethal impacts are not observed. Diatoms, by displaying deformities (teratologies) in their valves, have the potential to reflect sub-lethal responses to environmental stressors such as metals and organic compounds. For this reason, there is great interest in using diatom morphological aberrations in biomonitoring. However, the detection and mostly the quantification of teratologies is still a challenge; not all studies have succeeded in showing a relationship between the proportion of abnormal valves and contamination level along a gradient of exposure. This limitation in part reflects the loss of ecological information from diatom teratologies during analyses when all deformities are considered. The type of deformity, the severity of aberration, species proneness to deformity formation, and propagation of deformities throughout the population are key components and constraints in quantifying teratologies. Before a metric based on diatom deformities can be used as an indicator of contamination, it is important to better understand the “ecological signal” provided by this biomarker. Using the overall abundance of teratologies has proved to be an excellent tool for identifying contaminated and non-contaminated environments (presence/absence), but refining this biomonitoring approach may bring additional insights allowing for a better assessment of contamination level along a gradient. The dilemma: are all teratologies significant, equal and/or meaningful in assessing changing levels of contamination? This viewpoint article examines numerous interrogatives relative to the use of diatom teratologies in water quality monitoring, provides selected examples of differential responses to contamination, and proposes solutions that may refine our understanding and quantification of the stress. This paper highlights the logistical problems associated with accurately evaluating and interpreting teratologies and stimulates more discussion and research on the subject to enhance the sensitivity of this metric in bioassessments.