Can Hediste diversicolor (Nereidae, Polychaete) be considered a good candidate in evaluating PAH contamination? A multimarker approach.

The aim of this study was to develop a preliminary characterization of the biological responses of Hediste diversicolor to polycyclic aromatic hydrocarbons (PAHs) under controlled laboratory conditions. In order to test the effects of PAH exposure, a battery of biomarkers was applied to the polychaetes by exposing them to sublethal concentrations of benzo[a]pyrene (0.1 and 0.5 mg L(-1)) for 10d under laboratory conditions. The battery of biomarkers tested included oxidative stress biomarkers (glutathione content, enzymatic activities of catalase, glutathione S-transferases, glutathione reductase, glutathione peroxidases), total oxyradical scavenging capacity (TOSC) toward peroxyl and hydroxyl radicals and activity of acyl CoA oxidase (AOX) as a marker of peroxisome proliferation measured in the entire body; lipofuscin and neutral lipid accumulations and levels of Ca(2+)-ATPase activity analyzed in the intestinal epithelium; lysosomal membrane stability and genotoxic effects measured as DNA strand breaks and frequency of micronuclei in coelomocytes. Chemical analyses were also carried out to verify the polychaete's benzo[a]pyrene (B[a]P) bioaccumulation levels after the exposure period. The results obtained indicate that B[a]P caused significant changes in most of the parameters measured in H. diversicolor. Biological responses to the organic compound were particularly significant for the biomarkers measured in the intestinal epithelium and in coelomocytes, emphasizing that these tissues were more affected during our experimental conditions. Considering the key trophic role of this benthic species in estuarine and coastal ecosystems, this study confirmed that H. diversicolor is an appropriate bioindicator of organic contamination.

Mucilage impact on gorgonians in the Tyrrhenian sea.

The mucilage phenomenon has affected the Tuscan Archipelago since its first appearance (1991) in the Tyrrhenian Sea (Mediterranean Sea) [Innamorati M, Raddi E, Buzzichelli A, Melley S, Demoulin M. Le mucillaggini nel Mar Tirreno. Biol Mar Suppl Notiz 1992;1:23-26; Sartoni G, Sonni C. Tribonema marinum J. Feldmann e Acinetospora crinita (Carmichael) Sauvageau nelle formazioni mucillaginose bentoniche osservate sulle coste toscane nell'estate 1991. Inf Bot Ital 1991;23:23-30; Sartoni G, Cinelli F, Boddi S. Ruolo di Tribonema marinum J. Feldmann ed Acinetospora crinita (Carmichael) Sauvageau negli aggregati mucillaginosi bentonici delle coste toscane. Biol Mar Suppl Notiz 1993;1:31-34]. Seasonally, these mucous aggregates become very common in the benthic domain. The gorgonians are the most exposed organisms because they provide the best support for mucilage growth; indeed, their long branches positioned in orthogonally with respect to the current so as to capture plankton, also trap the filamentous mucilage present in the water. A 3-year monitoring programme at Capo Calvo (Island of Elba) was carried out in order to study the appearance of the mucilage phenomenon and its impact on three species of gorgonians (Eunicella cavolinii, Eunicella singularis, and Paramuricea clavata). The composition of mucilage and the gorgonian recovery capacity, when damaged, were investigated. During the first year of study (1999), no relevant interactions between gorgonians and mucilages were recorded. Instead, massive presence of mucilages causing different types of damage to the different gorgonian species investigated was recorded during the second (2000) and third year (2001). The type and the extent of the impact of mucilages also depend on the season. Three species of algae (Nematochrysopsis marina, Chrysonephos lewisii and Acinetospora crinita) constitute the principal components of the mucilaginous aggregates. In general, the first two species occur during the spring season, down to 20 m, while A. crinita occurs at greater depths. In July, when the mucilages reach their maximum development, C. lewisii is the predominant species. This species mainly affects E. cavolinii and E. singularis while A. crinita mainly affects P. clavata, which colonizes greater depths.