Comparison of cytochemical procedures to estimate lysosomal biomarkers in mussel digestive cells

Enlargement and membrane destabilisation in digestive cell lysosomes of mussels are biomarkers of pollution effect. Cytochemical methods are currently applied to determine lysosomal membrane stability (LMS) and lysosomal structural changes (LSC). LMS, determined after grading N-acetyl-beta-hexosaminidase activity on cryotome sections of digestive gland, is measured as labilisation period (LP). LSC, determined after image analysis of cryotome sections where beta-glucuronidase activity is revealed, are measured as lysosomal volume (Vv), surface (Sv), numerical (Nv) densities and surface-to-volume ratio (S/V). Both methods have now been compared in a field study. Mussels were collected from Biscay Bay (Plentzia, reference; Muskiz, moderately polluted) and North Aegean Sea (Olympiada, reference; Limani, heavily polluted). Higher Vv and Sv and lower S/V and LP were recorded in polluted sites than in reference sites. Significant correlations with LP were found for Vv and S/V. The cost/effectiveness and environmental significance of both methods are discussed.

Lysosomal enlargement in digestive cells of mussels exposed to cadmium, benzo[a]pyrene and their combination

Digestive cell lysosomes in mussels are known to respond to individual organic chemicals and metals after experimental exposure under laboratory conditions but reports dealing with the response to mixtures of pollutants are scarce. The aim of the present investigation was to compare the lysosomal responses elicited by exposure to a model organic chemical compound (benzo(a)pyrene, B[a]P), a model toxic metal (Cd) and their combination (B[a]P+Cd) under controlled laboratory conditions. Dimethylsulfoxide (DMSO) was used as vehicle to dissolve organic chemicals into seawater. Control mussels were either kept untreated in clean seawater or treated with DMSO. Digestive glands were excised on Day 21. beta-Glucuronidase activity was demonstrated in 8 mum cryotome sections. Lysosomal volume, surface and numerical densities (Vv, Sv and Nv), and surface-to-volume ratio (S/V) were quantified by image analysis. Lysosomal enlargement was evident in digestive cells of mussels exposed to either Cd, B[a]P or B[a]P+Cd. Such enlargement was more marked after exposure to B[a]P+Cd than to B[a]P, but did not reach the levels recorded after Cd exposure. It seems therefore that the presence of B[a]P reduced to some extent the effects of Cd on digestive cell lysosomes in mussels.

Use of polyclonal antibodies for the detection of changes induced by cadmium in lysosomes of aquatic organisms

Lysosomal responses are widely accepted cellular effect biomarkers of general stress. Up to now, these biomarkers have been analysed by means of conventional techniques based on enzyme histochemical methods, where lysosomal enzymes such as acid phosphatase and beta-glucuronidase (beta-GUS) have been employed as markers of lysosomes. The aim of the present work was to develop more advanced and sensitive methods based on the use of polyclonal antibodies to measure lysosomal enzymes in different sentinel organisms. For this purpose, we have studied the cross-reactivity of two commercial polyclonal antibodies against the lysosomal enzymes acid phosphatase and beta-GUS with molluscan digestive gland by means of immunoblotting and immunohistochemistry. The antibody against acid phosphatase cross-reacted specifically with the lysosomal fraction of the digestive gland, while unspecific immunoreaction occurred with digestive gland whole homogenates and tissue sections. The antibody against beta-GUS cross-reacted specifically with digestive gland whole homogenates and tissue sections. The cross-reactivity of this antibody was tested also in crab hepatopancreas and mullet liver where the same successful results were obtained. The second aim of the present study was to test if the immuno-based approach was sensitive enough to detect lysosomal alterations provoked by contaminants. For this purpose two experiments were carried out with mussels treated with cadmium in two ways: in vivo treatment by injection and in vitro treatment using digestive gland explants. Afterwards immunoblotting studies with the antibody against beta-GUS were applied and immunoreactive bands were quantified by means of a gel analysis programme. We found that beta-GUS protein levels were higher in treated mussels when compared with controls in either in vivo or in vitro treatments. All these data suggest that the polyclonal antibody against beta-GUS is adequate to be used in immuno-based approaches to detect contaminant-induced lysosomal alterations.

Autometallographical localisation of Cu and Zn within target cell compartments of winkles following exposure to Cu&Zn mixtures

This investigation attempts to determine the usefulness of autometallography to localise particular metals in certain key tissues of molluscs exposed to metal mixtures. For this purpose, winkles (Littorina littorea) removed from shell were exposed to very high concentrations of either copper (Cu), zinc (Zn) or a mixture of both metals (Cu&Zn) dissolved in sea-water for short periods of time. Protein-bound metals were detected by autometallography as black silver deposits (BSD) on histological sections of gills, foot, mantle, digestive gland/gonad complex, stomach and kidney. Copper was localised within cytoplasmic granules of gill ciliated cells, nephrocytes and stomach epithelial cells as well as within digestive cell lysosomes. Zinc was essentially found in the basal lamina (histological sense) of gill, stomach, kidney and digestive gland epithelia. BSD were also evidenced in cytoplasmic granules of pore cells present in parenchymal connective tissue of mantle, foot, gill, digestive gland and stomach. Copper and zinc concentrations were additionally calculated for the whole soft body as well as for certain organs by atomic absorption spectrophotometry (AAS). According to AAS, a synergistic phenomenon would contribute to increase the rate of Cu and Zn accumulation in presence of each other. However, after exposure to Cu&Zn autometallography did not evidence any synergistic phenomenon, and Cu and Zn were localised in their respective accumulation sites. In conclusion, autometallography might indicate the presence of certain metals in the environment irrespective of factors, such as "metal-metal interaction-like" phenomena, affecting metal concentrations in soft tissues.

Immunochemical localisation of proliferating cells in mussel digestive gland tissue

The distribution of proliferating cells in the digestive gland of the common marine mussel, Mytilus galloprovincialis Lmk, was investigated by means of immunochemical techniques employing PC10, a commercial monoclonal antibody to the proliferating cell nuclear antigen (PCNA). Immunoblot analysis of digestive gland whole homogenates revealed a single crossreactive band of 36-37 kDa, identical to the corresponding protein of rat liver and murine melanoma cells. A band of slightly higher electrophoretic mobility (34-35 kDa) was found in fish liver. In mussel digestive gland, the samples obtained from young specimens presented a more intense signal for PCNA than in those obtained from old mussels, suggesting that the digestive gland cells of young mussels exhibit a higher proliferative activity. In paraffin sections, PC10 specifically labelled nuclei of all cell types, but only a smaller number of cells lining the different digestive epithelia. PCNA expression was more intense in digestive cells than in basophilic cells. Hemocytes circulating along the interdiverticular spaces also presented immunoreactive nuclei. Electron microscopy revealed a specific and moderate PC10 labelling in nuclei. Thus, single gold particles appeared disseminated throughout the nuclei with accumulations of particles in the sites of DNA replication. Taken together, these data reveal that the capacity to proliferate resides within all cell types in the digestive diverticula and do not support the hypothesis of the existence of one stem cell in this epithelium. As opposed to the hepatopancreas of the crab, Carcinus maenas, where mitotic figures and PCNA immunoreactivity are only observed in the embryonic cells within the distal portions of the digestive diverticula, apparently there are not discrete regions of cell proliferation in the digestive gland of mussels.