Fig. 2. Summary of the results demonstrating that SPATT passive sampling could advantageously contribute to the reinforcement of ciguateric
risk assessment and management programmes as a supplementary tool.
or of very low densities of toxic Gambierdiscus cells. However, CTXs were
detected in numerous fish collected in
Kaukura Island (CBA-N2a), suggesting
that blooms of toxic Gambierdiscus had
previously occurred in this area, leading to the bioaccumulation of CTXs in
marine products, but had disappeared
at the time of the SPATT devices deployment. Another explanation could
be that SPATT devices allow for the detection of CTXs in the field only when
high levels of CTXs are dissolved in the
seawater and are thus relevant only in
highly ciguateric locations.
In all cases, these results (summarized in Fig. 2) confirmed the ability of
SPATT technology to detect CTXs in the
field and thus emphasize the relevance
of this toxin-based technique as a useful supplementary tool when assessing
the risks associated with Gambierdiscus
proliferation in locations highly prone
to ciguatera. It should be highlighted
that SPATT devices are only able to give
indications of the presence of Gambierdiscus cells (detection of MTX3) and
their toxicity (detection of CTXs) in an
area at a given time, but they are not
effective to guarantee the edibility of
HARMFUL ALGAE NEWS NO. 60 / 2018
marine products that could have bio-accumulated toxins in their tissues. The
simplicity, low-cost and logistical advantages (e.g. storage and transport) offered by these easy-to-use devices make
SPATT technology a valuable tool well
adapted to the survey of CFP risk, most
notably in widely dispersed and remote
sampling locations in PICTs. Moreover,
given the risk of simultaneous accumulation of multiple biotoxins in seafood
products in tropical environments, the
use of SPATT technology, when combined with downstream analyses such
as LCMS/MS multi-toxin screenings,
also offers promising prospects in the
framework of emerging toxins surveillance.
Acknowledgments
This work was supported by funds from
France and French Polynesia (Contrat
de Projets Caractérisation et gestion
des risques environnementaux et sanitaires liés au développement de phytobenthos ciguatérigène en Polynésie
française CARISTO-Pf - n 7937/MSR/
REC; Fonds Pacifique Ciguatera: a neglected disease of the South Pacific - n
CZT 1065 01 T).
References
1. Dickey RW & Plakas SM 2010. Toxicon
56: 123-136
2. Roué M et al 2016. Harmful Algae 57:
78-87
3. Darius et al 2018. Toxins 10(1): 2
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5. Skinner MP et al 2011. PLoS Negl Trop
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Authors
Mélanie Roué, Institut de Recherche pour le
Développement (IRD) - UMR 241-EIO, PO Box
53267, 98716 Pirae, Tahiti, French Polynesia
Hélène Taiana Darius, Clémence Gatti &
Mireille Chinain, Institut Louis Malardé
(ILM), Laboratory of Toxic Microalgae - UMR
241-EIO, PO Box 30, 98713 Papeete, Tahiti,
French Polynesia
David Timothy Harwood, Cawthron Institute,
Private Bag 2, Nelson, 7010, New Zealand
Corresponding author: melanie.roue@ird.fr
9
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