To study the effects of sublethal doses of mercury on corals, colonies of Porites astreoides (Lamarck) were exposed to nominal concentrations of 0.01, 0.1 and 0.5 mg Hg l -1 using semi-static, chronic bioassays for up to 15 d, with HgCl 2 administered by pulses every 3 d (mean concentration in the water was 0.004, 0.037 and 0.180 mg Hg l -1 , respectively). While total Hg in the corals was directly proportional to Hg exposure, analysis of the different coral compartments (polyps, zooxanthellae and skeleton) showed that zooxanthellae and the skeleton accumulated Hg in direct relation to Hg exposure, but polyp tissue accumulated more Hg at 0.1 than at 0.5 mg Hg l -1 . This suggests saturation of Hg only in polyps and/or activation of mechanisms of detoxification. Within a colony, the Hg concentration per unit area of coral surface differed between compartments as follows: zooxanthellae > polyp > skeleton. Colonies exposed to the highest Hg concentration accumulated 1.738 µg Hg cm -2 , 89% of which was found in zooxanthellae, 7% in polyps and 4% in the skeleton. Polyp biomass (dry weight and protein content), zooxanthellae biomass (cell density and protein content), and pigment concentration per unit area of coral surface decreased with Hg exposure. The bioconcentration factor ([Hg] in organism/ [Hg] in water) was inversely related to the Hg concentration in water. The capacity of zooxanthellae and the skeleton to concentrate Hg and the decrease in zooxanthellae density support the hypothesis that polyps may divert Hg to these 2 coral compartments as a detoxifying mechanism.KEY WORDS: Mercury · Bioconcentration · Bioassays · Sub-lethal exposure · Hard corals · Porites · Caribbean
Resale or republication not permitted without written consent of the publisherMar Ecol Prog Ser 267: [133][134][135][136][137][138][139][140][141][142][143] 2004 ticular concern due to its extensive use in gold mining and its high toxicity (Lacher & Goldstein 1997). It is estimated that atmospheric input of Hg has tripled over the past 150 yr, and that two-thirds of the current total is of anthropogenic origin, while one-third is from natural sources (Morel et al. 1998). On the west coast of Venezuela, Hg contamination has been a potential hazard for marine communities for several decades. Sources include a chlor-alkali plant, which operated in Golfo Triste until the mid-1970s (see Iglesias & Penchaszadeh 1983, Pérez 1995 for further details), and an oil refinery and a petrochemical complex, which still operate here. This area is also affected by the discharge of various rivers with catchments encompassing agricultural lands. All these activities contribute to an increase in anthropogenic sources of metals, and Hg in particular. At the western end of Golfo Triste, Hg levels in seawater, marine invertebrates, seagrasses and the sediments at the coral reefs of Parque Nacional Morrocoy (Iglesias & Penchaszadeh 1983, Pérez 1995, García et al. 1998 indicated that the knowledge of Hg concentration and its sublethal effects on orga...