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Study Organism and Conditions

Juvenile pink snapper (Pagrus auratus), sexually immature, were collected from a local hatchery, Fremantle TAFE Centre, Western Australia. After being acclimated in 1001 seawater tanks, the experimental groups were exposed to the weathering muds [Pg.315]

Physicochemical parameters of the water (salinity, pH, and temperature) from all treatment tanks, and also heavy metal concentrations, were measured on a daily basis. [Pg.316]

Exposure groups N Total weight (g) Total length (cm) Condition factor (CF) Liver somatic index (LSI) [Pg.317]

Fish exposed to the reformulated Syndrill 80 20 (Mod) did not exhibit biliary metabolite fluorescence at the naphthalene wavelength relative to the negative control group (p = 0.302), whereas the fish exposed to the original Syndrill 80 20 [Pg.317]

To investigate further the chemical characteristics of potential alternative emulsifiers, the water-soluble fractions (WSFs) of each emulsifier were measured [61]. The samples were analyzed for total recovered hydrocarbons (TRH) in the C10-C36 region and PAHs [3, 62]. The chemical analysis of the emulsifier WSFs did not detect PAHs. Consequently, in the future, use of low-fluorescence emulsifiers in the reformulated Syndrill 80 20 (Mod) will allow the measurement of biliary fluorescence as a biomarker of exposure in field-caught fish attracted to cutting piles, with any detected fluorescence eliminating the drilling mud Syndrill 80 20 (Mod) as a source of fluorescent metabolites in the biliary secretions. [Pg.319]


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