Session 5
The Hydra assay as an early screen for teratogenic potential

https://doi.org/10.1016/0887-2333(90)90119-EGet rights and content

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    These cells contain different types of granules whose content (glycans, glycoproteins and peroxidase) is in part secreted outside in the external environment [20,21]. We first investigated the potential toxic effect and more broadly the biocompatibility of ETE-S, by monitoring and quantifying morphological alteration induced at variable dose and exposure time, according to well established methods [11,22,23]. Living polyps were incubated with increasing doses of ETE-S, from 10 μg/mL to 1 mg/mL, the effective dose used in plant systems (Fig. S1) [8].

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  • The use of ephyrae of a scyphozoan jellyfish, Aurelia aurita, in the aquatic toxicological assessment of Macondo oils from the Deepwater Horizon incident

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    Such organisms may be exposed to chemicals via multiple pathways, including uptake of dissolved compounds through diffusion, dietary uptake or contact with contaminated sediments and suspended particles (Faimali et al., 2014). Until recently, the predominantly used benthic cnidarians used in ecotoxicological assessments and include hydras (Wilby and Tesh, 1990; Kusui and Blaise, 1999; Pascoe et al., 2003), sea anemones (Mercier et al., 1997) and scleractinian corals (Epstein et al., 2000; Negri and Heyward, 2001; Tarrant et al., 2004; Jones, 2005). The GOM supports one of the most diverse cnidarian populations in the world, with conservative estimates of over 115 epipelagic species (Phillips, 1971; Graham, 2001).

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    Among the cnidarians only benthic organisms have been used recently in toxicity testing, including hydras, colonial hydroids, sea anemones, and scleractinian corals and sub-lethal endpoints including budding, regeneration, gametogenesis, mucus production and larval metamorphosis have been developed. The Hydra spp. are the most widely used cnidarians in toxicity testing (Wilby and Tesh, 1990; Kusui and Blaise, 1999; Pollino and Holdway, 1999; Karntanut and Pascoe, 2000; Holdaway et al., 2001; Pascoe et al., 2003), other cnidarians are occasionally used (e.g., anemones, Mercier et al., 1997; colonial hydroids, Chicu et al., 2000) in toxicity testing with dissolved contaminants. As regards hydras, the most commonly observed endpoints are sub-lethal, such as budding, polyp structure and polyp regeneration.

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