Toxicology tailored low density oligonucleotide microarray for the thicklip grey mullets (Chelon labrosus): Biomarker gene transcription profile after caging in a polluted harbour.

In aquatic organisms inhabiting polluted waters genes are activated to build an adaptive/compensatory defence against the possible effects of pollutants. Such responses can be used as biomarkers of exposure to chemical compounds, outlining the molecular mechanisms activated under specific pollution scenarios. With the aim of exploiting such approach in environmental health assessment, toxicologically relevant gene fragments were sequenced in the thicklip grey mullet (Chelon labrosus) and a toxicologically tailored low-density (160 genes) oligonucleotide microarray was customised. The tool was validated comparing organ/sex specific gene expression profiles and characterising responses under laboratory exposure to model chemicals. Finally, juvenile mullets were caged in a polluted harbour and hepatic gene expression profiles analysed after 5 and 21 days of deployment. Cages were deployed in the inner (IH) and outer (OH) Pasaia harbour, Bay of Biscay. Mussels (Mytilus galloprovincialis) were also caged as biological matrix for chemical bioaccumulation analysis and stress biomarkers measurements. Slightly higher concentrations of chemicals (metals, tributyltin, PAHs, phthalates) were quantified in IH than in OH, fish bile metabolites also revealing higher availability of PAHs in IH. Lysosome membrane stability in mussels was reduced, indicating stress condition in both sites. The developed microarray discriminated mullets showing distinctive expression profiles depending on site and deployment time. Genes related to immune and hypoxia responses were regulated comparing IH and OH at day 5. Phase I and II biotransformation genes, such as cyp2, cyp3 and ugt, were up-regulated in IH, together with the aryl hydrocarbon receptor 2 (ahr2) and the ahr repressor. Similarly, TBT-binding proteins and genes involved in lipid metabolism (pparγ, cyp7) were up-regulated with deployment time. Even if nowadays higher throughput approaches for gene expression analyses are available, the developed mullet tool constitutes a comprehensive tool to assess molecular responses of mullets exposed to pollutants, although it remains to be explored whether it can be applied to assess pollutant exposure in active pollution monitorings and in environmental health assessment.

Assessment of the effects of discontinuous sources of contamination through biomarker analyses on caged mussels.

The present study analysed potential adverse effects of discontinuous sources of contamination, namely the discharge of a combined sewer overflow (CSO) and of runoff in an urban area, the Bay of Santander (North Iberian Peninsula). Water samples and caged mussels were used to analyse concentrations of contaminants and biological responses. Mussels (Mytilus galloprovincialis) were transplanted to a marina receiving runoff from a petrol station and to a CSO discharge site. Samples were collected in synchrony with heavy rains along 62days. Lysosomal membrane stability (LMS) and acyl-CoA oxidase (AOX) activity were measured as core biomarkers and were analysed at all sampling times. Histopathology of digestive gland and gonads, transcription levels of vitellogenin gene, volume density of black silver deposits and micronuclei formation were measured at initial and final stages of the transplant. Chemical analyses of metals, polycyclic aromatic hydrocarbons (PAHs) and endocrine disruptors were performed in water samples and mussel flesh. Mussels accumulated low concentrations of contaminants, which is in accordance with results obtained from exposure biomarkers. AOX activity decreased in all transplanted mussels after the first heavy rain, but this change seems to be related to the seasonal pattern of the enzyme activity. Mussels located close to the CSO discharge site showed a reduction in LMS after the first rain event, when compared to mussels before the transplant and to mussels from the reference location. However, this was attributable to natural environmental changes rather than to pollution. Values of the rest of analysed biomarkers were below threshold values reported for the study area.

Lysosomal responses to different gold forms (nanoparticles, aqueous, bulk) in mussel digestive cells: a trade-off between the toxicity of the capping agent and form, size and exposure concentration.

Gold nanoparticles (NPs) are increasingly used in technological materials and consumer products and may have toxicological characteristics distinct from bulk and aqueous gold. The aim of this work was to understand the effects of Au NPs especially, how the form, the size and the coating influence bioaccumulation/biodistribution and toxicity of NPs in mussels, Mytilus galloprovincialis. Mussels were exposed for 3 d to concentrations of Au (0.75, 75 and 750 µg Au/l) supplied as Au-Cit NPs (5 and 40 nm; Au5-Cit and Au40-Cit), bulk and aqueous Au (HAu(III)Cl4), and to the capping agent (Na-citrate) in doses used in the formulation of NPs (0.005, 0.5, 5 mg/l). Citrate-stabilised NPs formed stable suspensions of aggregates in seawater (SW) available for mussels. Au accumulation in soft tissues was similar in Au40-Cit and aqueous Au exposed mussels, lower in Au5-Cit and negligible after bulk exposure. Au NPs were identified (X-ray microanalysis) in different compartments of the endolysosomal system in digestive cells, and small size NPs (5 nm) were more accumulated than 40 nm NPs, aqueous and bulk. The degree of lysosomal membrane destabilisation was related with intralysosomal metal accumulation and depended on the form, NP size (Au5-Cit > Au40-Cit > aqueous > bulk) and concentration. Citrate alone provoked extreme reduction in lysosomal membrane stability. Toxicopathic alterations were recorded in digestive gland cells (vacuolisation, swollen RER, connective tissue disruption and cell death) especially in mussels exposed to 40 nm NPs. Deleterious effects resulted from digestive tract obliteration (agglomerates) and digestion malfunction. The toxic effect of Au-Cit NPs was influenced both by NP size, capping agent composition and the dose of capping agent carried by NPs, which was size dependent.

Effects of PVP/PEI coated and uncoated silver NPs and PVP/PEI coating agent on three species of marine microalgae.

In the last years, applications for silver nanoparticles (Ag NPs) continue to increase together with the concerns about their potential input and hazards in aquatic ecosystems, where microalgae are key organisms. The aim of the present study was to assess the relative sensitivity of three marine microalgae species with differences in cell wall composition/structure exposed to Poly N-vinyl-2-pirrolidone/Polyethyleneimine (PVP/PEI) coated 5nm Ag NPs and uncoated 47nm Ag NP. As limited attention has been paid to the role of coating agents in NP toxicity, the effect of PVP/PEI alone was also evaluated. After 72h in artificial seawater, 47nm Ag NPs formed around 1400nm size aggregates while PVP/PEI coated 5nm Ag NPs reached around 90nm. Ag+ release in seawater was around 3% for 47nm Ag NPs and 30% for PVP/PEI coated 5nm Ag NPs. PVP/PEI coated 5nm Ag NP aggregates entrapped the algal cells in a network of heteroaggregates, while uncoated 47nm Ag NPs interacted to a lesser extent with algae. The concentration of PVP/PEI coated 5nm Ag NPs that exerted the median effect (EC50) on algae growth pointed out differences in algae sensitivity: T. suecica was about 10 times more sensitive than I. galbana and P. tricornutum. Further, the coating agent alone was as toxic to algae as PVP/PEI coated 5nm Ag NPs, suggesting that presence of the coating agent was the main driver of toxicity of coated NPs. Uncoated 47nm Ag NPs instead, showed similar toxicity towards algae although P. tricornutum was slightly less sensitive than T. suecica and I. galbana, which agrees with the presence of a resistant silicified cell wall in the diatom. The present work demonstrates differences in sensitivity of three marine microalgae, possibly related to their cell surface and size characteristics.

Digestive cell lysosomes as main targets for Ag accumulation and toxicity in marine mussels, Mytilus galloprovincialis, exposed to maltose-stabilised Ag nanoparticles of different sizes.

Bioavailability and toxicity of maltose-stabilised AgNPs of different sizes (20, 40 and 100 nm) in mussels were compared with bulk and aqueous forms of the metal through a two-tier experimental approach. In the first tier, mussels were exposed for 3 d to a range of concentrations (0.75, 75, 750 µg Ag/l) in the form of Ag20-Mal, Ag40-Mal, Ag100-Mal, bulk Ag and aqueous Ag (as AgNO3), as well as to the concentrations of maltose used in the formulation of NPs. Mortality, bioaccumulation, tissue and cell distribution and lysosomal responses were investigated. In the second tier, mussels were exposed for 21 d to Ag20-Mal, Ag100-Mal, bulk Ag and aqueous Ag at the lowest effective concentration selected after Tier 1 (0.75 µg Ag/l), biomarkers and toxicopathic effects were investigated. Aqueous Ag was lethal within 3 d at 75 µg Ag/l; Ag NPs or bulk Ag did not produce significant mortality at 750 µg Ag/l. Ag accumulation was limited and metallothionein gene transcription was not regulated although metal accumulation occurred in digestive, brown and stomach epithelial cells and in gut lumen after exposure to AgNPs and aqueous Ag starting at low concentrations after 1 d. Electrondense particles (<10 nm) in lysosomes and residual bodies after exposure to AgNPs contained Ag and S (X-ray). Intralysosomal metal accumulation and lysosomal membrane destabilisation were enhanced after exposure to all the forms of Ag and more marked after exposure to Ag20-Mal than to larger NPs. 21 d exposure to AgNPs provoked digestive cell loss and loss of digestive gland integrity, resulting in atrophy-necrosis in digestive alveoli and oedema/hyperplasia in gills (Ag NP), vacuolisation in digestive cells (aqueous Ag) and haemocyte infiltration of connective tissue (all treatments). Intralysosomal metal accumulation, lysosomal responses and toxicopathic effects are enhanced at decreasing sizes and appear to be caused by Ag+ ions released from NPs, although the metal was not substantially accumulated.

Nanoparticle size and combined toxicity of TiO2 and DSLS (surfactant) contribute to lysosomal responses in digestive cells of mussels exposed to TiO2 nanoparticles.

The aim of this investigation was to understand the bioaccumulation, cell and tissue distribution and biological effects of disodium laureth sulfosuccinate (DSLS)-stabilised TiO2 nanoparticles (NPs) in marine mussels, Mytilus galloprovincialis. Mussels were exposed in vivo to 0.1, 1 and 10 mg Ti/L either as TiO2 NPs (60 and 180 nm) or bulk TiO2, as well as to DSLS alone. A significant Ti accumulation was observed in mussels exposed to TiO2 NPs, which were localised in endosomes, lysosomes and residual bodies of digestive cells, and in the lumen of digestive tubules, as demonstrated by ultrastructural observations and electron probe X-ray microanalysis. TiO2 NPs of 60 nm were internalised within digestive cell lysosomes to a higher extent than TiO2 NPs of 180 nm, as confirmed by the quantification of black silver deposits after autometallography. The latter were localised mainly forming large aggregates in the lumen of the gut. Consequently, lysosomal membrane stability (LMS) was significantly reduced upon exposure to both TiO2 NPs although more markedly after exposure to TiO2-60 NPs. Exposure to bulk TiO2 and to DSLS also affected the stability of the lysosomal membrane. Thus, effects on the lysosomal membrane depended on the nanoparticle size and on the combined biological effects of TiO2 and DSLS.

Relationships between lines of evidence of pollution in estuarine areas: Linking contaminant levels with biomarker responses in mussels and with structure of macroinvertebrate benthic communities.

Data obtained in a pollution survey performed in estuarine areas were integrated using multivariate statistics. The sites selected for the study were areas affected by treated and untreated urban discharges, harbours or industrial activities as well as reference sites. Mussels were transplanted to each site and after different times of exposure, samples of water, sediments and mussels were collected. Biomarkers were analysed on mussels after 3 and 21 days of transplant whereas concentrations of contaminants were measured in water, sediments and mussels after 21 days of transplant. The structure of macroinvertebrate benthic communities was studied in sediment samples. Studied variables were organised into 5 datasets, each one constituting a line of evidence (LOE): contaminants in water, contaminants in sediments, contaminants accumulated by transplanted mussels, biomarkers in transplanted mussels and changes in the structure of macroinvertebrate benthic communities of each sampling site. Principal Component Analysis (PCA) identified the variables of each LOE best explaining variability among sites. In order to know how LOEs relate to each other, Pearson's correlations were performed. Contaminants in sediments were not correlated with the rest of LOEs. Contaminants in water were significantly correlated with contaminants and biomarkers in mussels and with structure of macroinvertebrate benthic communities. Similarly, significant correlations were found between contaminants and biomarkers in mussels and between biomarkers in mussels and structure of macroinvertebrate benthic communities. In conclusion, biomarker responses give relevant information on pollution in estuarine areas and provide a link between chemical and ecological statuses of water bodies in the context of the Water Framework Directive.

Measuring biological responses at different levels of organisation to assess the effects of diffuse contamination derived from harbour and industrial activities in estuarine areas.

To evaluate the effects of diffuse contamination, biological measurements were applied in a scrap cargo harbour, a marina and an industrial area. Metal accumulation and biomarkers (survival in air, digestive gland and gonad histopathology, lysosomal membrane stability, intralysosomal metal accumulation, transcription of vitellogenin and MT20, peroxisome proliferation and micronuclei formation) were measured in transplanted mussels, together with metrics of benthic invertebrates. Benthic species were classified into ecological groups and univariate indexes were calculated. The marina showed high richness (16) and percentage of opportunistic species (55.1%) and low metal accumulation. Mussels in the scrap cargo harbour showed high metal accumulation, up-regulation of MT20 transcription, reduced health status (LP<6 min) and increased micronuclei frequencies (up to 11.3‰). At the industrial area, low species richness (4) and badly organised assemblages were detected and chemical analyses indicated significant amounts of bioavailable metals. Overall, selected biological measurements showed potential for the assessment of diffuse contamination.

Cell biology of peroxisomes and their characteristics in aquatic organisms.

The general characteristics of peroxisomes in different organisms, including aquatic organisms such as fish, crustaceans, and mollusks, are reviewed, with special emphasis on different aspects of the organelle biogenesis and mechanistic aspects of peroxisome proliferation. Peroxisome proliferation and peroxisomal enzyme inductions elicited by xenobiotics or physiological conditions have become useful tools to study the mechanisms of peroxisome biogenesis. During peroxisome proliferation, the induction of peroxisomal proteins is heterogeneous, enzymes that show increased activity being involved in different aspects of lipid homeostasis. The process of peroxisome biogenesis is coordinately triggered by a whole array of structurally dissimilar compounds known as peroxisome proliferators, and investigating the effect of some of these compounds that commonly appear as pollutants in the environment on the peroxisomes of aquatic animals inhabiting marine and estuarine habitats seems interesting. It is also important to determine whether peroxisome proliferation in these animals is a phenomenon that might occur under normal physiological or season-related conditions and plays a metabolic or functional role. This would help set the basis for understanding the process of peroxisome biogenesis in aquatic animals.

Modulation of peroxisome proliferator-activated receptors (PPARs) by PPAR(alpha)- and PPAR(gamma)-specific ligands and by 17beta-estradiol in isolated zebrafish hepatocytes.

Peroxisome proliferation is a phenomenon occurring when responsive animals are exposed to certain compounds so-called peroxisome proliferators and is regulated through a nuclear receptor named peroxisome proliferator-activated receptor (PPAR). PPAR family members exhibit a strong binding affinity for both saturated and unsaturated fatty acids. Activators of PPAR(alpha) include a variety of endogenously present fatty acids, leukotrienes and hydroxyeicosatetraenoic acids (HETEs) and clinically used drugs, such as fibrates. PPAR(beta) activators include fatty acids, prostaglandin A2 (PGA2) and prostacyclin (PGI2). PPAR(gamma) is the most selective receptor and, among others, 15-deoxy-Delta(12,14) prostaglandin J2 (PGJ2) has been described to be a PPAR(gamma)-specific ligand. The aim of the present study was to determine if known PPAR(alpha) and PPAR(gamma) ligands were able to alter the expression of these subtypes in an in vitro model of zebrafish primary hepatocyte culture. With this purpose, a PPAR(alpha) specific ligand (8S-HETE), a PPARgamma specific ligand (PGJ) and a peroxisome proliferator of the fibrate class (clofibrate) were selected. In addition, the female hormone 17beta-estradiol was also used as it is known to interact with PPARs. After cell exposure for 24 h, cells were immunohistochemically stained for both PPARs and immunolabeling was quantified as percentage of positive nuclei and cells. Levels of expression of PPARs were also measured by image analysis as grey level per cell. Expression was induced for both PPAR(alpha) and PPAR(gamma) by clofibrate (at 0.5 mM for PPAR(alpha) and at 1 and 2 mM for PPAR(gamma)), by HETE (1 microM), and by PGJ2 (0.3 and 1 microM for PPAR(alpha) and 0.3 microM for PPAR(gamma)). Expression of PPARgamma was also induced at 10 microM by 17beta-estradiol. The percentage of PPAR(alpha) positive nuclei increased significantly at 1 microM HETE and the percentage of PPAR(gamma) positive cells decreased at 10 microM 17beta-estradiol. As a conclusion, clofibrate, HETE and PGJ2 are able to induce expression of both PPAR(alpha) and PPAR(gamma) in zebrafish primary hepatocyte cultures. Further studies are needed to identify how the expression of different PPAR subtypes is regulated and to elucidate the implication of PPAR subtypes in zebrafish cell functions.

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.

Isolation and morphofunctional characterization of mussel digestive gland cells in vitro.

The aim of the present study was to isolate and characterize digestive gland cells of the bivalve mollusc Mytilus galloprovincialis Lmk. The digestive gland of bivalves is a complex organ composed of digestive and connective tissues but it is also invaded by the reproductive tissue as gametogenesis proceeds. The digestive tissue is comprised of stomach and intestinal epithelial cells, ciliated and non-ciliated duct cells, digestive cells and basophilic cells. the last two cell types are found lining the epithelium of the blind-ending digestive tubules and are the main focus of this study. Two different approaches were assayed for cell isolation, i.e., explant culture techniques and mechanical plus enzymatical digestion techniques. Cell viability was tested by trypan blue exclusion, neutral red uptake and ultrastructural analysis. The explant cultures were often contaminated with bacteria and spermatozoa and, moreover, cells migrating out of the explants possibly corresponded to hemocytes and not to digestive tissue cells. Mechanical plus enzymatical digestion with collagenase was concluded to be the method of choice for digestive cell isolation, with a percentage of about 30% of isolated cells corresponding to digestive cells. The ultrastructure of digestive cells isolated with the latter procedure closely resembled that of mussel digestive cells in vivo.

Peroxisomes in digestive gland cells of the mussel Mytilus galloprovincialis Lmk. Biochemical, ultrastructural and immunocytochemical characterization.

The present study was undertaken because of the paucity of information on peroxisomes in molluscs and the increasing importance of these organisms as sensitive indicators of environmental pollution. Peroxisomes were identified by electron microscopy in all three main cell types of the digestive gland of the bivalve mollusc Mytilus galloprovincialis Lmk. They stained weakly with the alkaline diaminobenzidine reaction but showed distinct immunolabeling with an antibody against mammalian catalase by the postembedding protein A-gold procedure. In addition, mussel digestive gland peroxisomes were isolated by differential and metrizamide-density gradient centrifugation, and a 30-fold enrichment of catalase and a 20-fold enrichment of palmitoyl-CoA oxidase was obtained over the initial homogenate. By Western blotting, isolated peroxisomes crossreacted with antibodies to catalase and, furthermore, specific and prominent labeling of isolated peroxisomes was also demonstrated in thin sections incubated with anti-catalase antibodies. These observations establish that peroxisomes in molluscan digestive gland contain the peroxisomal marker enzymes catalase and acyl-CoA oxidase and that they can be labeled by cytochemical and immunocytochemical techniques. Further studies of alterations of molluscan peroxisomes by environmentally relevant xenobiotics are warranted.

Immunocytochemical localization of a urate oxidase immunoreactive protein in the plasma membranes and membranes of the secretory/endocytic compartments of digestive gland cells of the mussel Mytilus galloprovincialis.

The subcellular compartmentalization of urate oxidase (UOX) in the digestive glands of mussels, Mytilus galloprovincialis Lmk, was studied by means of immunoblotting and immunocytochemistry, using an antibody raised in rabbit against rat liver UOX. Western blot analysis of subcellular fractions revealed an immunoreactive polypeptide with a molecular weight similar to the corresponding mammalian hepatic protein. This crossreactive polypeptide of 32 kDa was particle-bound yet not peroxisome-associated. In paraffin sections the antiserum specifically labeled the plasma membrane of the digestive gland epithelial cells and discrete regions within the perinuclear and apical portions of the digestive tubules and duct cells. By electron microscopy gold particles representing antigenic sites were found on the microvilli and the lateral plasma membrane as well as the membranes of the secretory/ endocytic compartments, that is, the Golgi complex, secretory and some endocytic vesicle membranes. Since the peroxisomal UOX-antibody exhibits a comparable immunoreactivity towards a urate-transporter channel protein in rat kidney proximal tubules and has been used for its molecular cloning (Leal-Pinto et al., 1997, J. Biol. Chem. 272, 617-625), we suggest that the membrane protein identified in mussel digestive glands could represent a homologous urate-transporter protein.

D-Aspartate oxidase and D-amino acid oxidase are localised in the peroxisomes of terrestrial gastropods.

D-Aspartate oxidase and D-amino acid oxidase were found in high activity in the tissues of representative species of terrestrial gastropods. Analytical subcellular fractionation demonstrated that both of these oxidases co-localised with the peroxisome markers, acyl-CoA oxidase and catalase, in the digestive gland homogenate. Electron microscopy of peak peroxisome fractions showed particles of uniform size with generally well preserved variably electron-dense matrices bounded by an apparently single limiting membrane. Many of the particles exhibited a core region of enhanced electron density. Catalase cytochemistry of peak fractions confirmed the peroxisome identity of the organelles. Peroxisome-enriched subcellular fractions were used to investigate the properties of gastropod D-aspartate oxidase and D-amino acid oxidase activities. The substrate and inhibitor specificities of the two activities demonstrated that two distinct enzymes were present analogous to, but not identical to, the equivalent mammalian peroxisomal enzymes.

Light microscopic catalase histochemistry in mussel digestive gland tissue.

Different light microscopical procedures for the histochemical demonstration of catalase were tested in cryostat sections of mussel digestive gland tissue by using both benzidine and diaminobenzidine (DAB) as hydrogen donors. The selected procedure, which was also applied to mouse liver for comparative purposes, consisted of incubation in media containing 0.2% DAB and 0.3% H2O2 at pH 10.4 for 35 min at 42 degrees C. Addition of 0.01 M imidazole to the incubation medium increased the staining intensity of the histochemical procedure. The positive reaction product was localized in epithelial cells lining the digestive tubules and the ducts. The histochemical reaction was inhibited partially by aminotriazole or sodium azide and disappeared completely by omission of H2O2 from the incubation medium. On the other hand, heat resistant non-enzymatic reactions were observed in sites known to contain lipofuscins such as epithelial cells of the gastrointestinal tract and connective tissue brown cells.

Cytochemical and histochemical aspects of the digestive gland cells of the mussel Mytilus galloprovincialis (L.) in relation to function.

The epithelium of the digestive tubules of the mussel Mytilus galloprovincialis is comprised of two cell types, namely digestive and basophilic cells. In basophilic cells, the secretory granules are beta-glucuronidase immunoreactive, a fact that enhances the hypothesis that beta-glucuronidase is synthesized in basophilic cells. A novel observation at the ultrastructural level is the pinocytic activity associated with the formation of coated pits. This observation constitutes direct evidence for endocytic processes taking place in basophilic cells. The use of cryostat sections from the same digestive tubules reveals, in many instances, a very pronounced neutral lipid accumulation in the same structures giving a positive reaction for N-acetyl-beta-hexosaminidase, indicating the association of those lipids with lysosomes. In some mussels, a high content of lipofuscin was observed in the lysosomes of the digestive cells. In these cases, the lysosomal structures show a limited neutral lipid content, and a weaker N-acetyl-beta-hexosaminidase reaction. In the digestive cells, the carbohydrate content of the lysosomes, and very well-developed canal system in the apical part of cells are discussed in relation to their function.

Comparative effects of cadmium, copper, paraquat and benzo[a]pyrene on the actin cytoskeleton and production of reactive oxygen species (ROS) in mussel haemocytes.

The immune defence of mussels is comprised of cell-mediated and humoral mechanisms, in which haemocytes or blood cells play a key role. Environmental pollutants such as metallic and organic xenobiotics exert immunotoxical effects on aquatic organisms. Some of these xenobiotics are known to give rise to highly reactive oxygen species (ROS), thereby leading to oxidative damage to tissue macromolecules including DNA, proteins and lipids. Previously we have detected enhancement of ROS production together with severe alterations in the actin cytoskeleton after exposure of mussel haemocytes to the carcinogenic polycyclic aromatic hydrocarbon benzo[a]pyrene (b[a]p). In a similar way, cadmium is also known to cause disruption of the actin cytoskeleton in mussel haemocytes, however it is not known whether this effect occurs by direct action or through ROS production. The aim of the present study was to decipher whether cytoskeletal alterations caused by Cd in mussel haemocytes are linked to increased ROS production. ROS-producing model compounds copper (Cu), paraquat and b[a]p were used in parallel experiments for comparative purposes. In all contaminant exposure experiments actin cytoskeleton appeared damaged. On the other hand, ROS production was increased in paraquat and b[a]p exposure experiments but decreased in haemocytes exposed to Cu while no significant effects were detected in Cd exposure experiments. In conclusion, it appears that deleterious effects of Cu and Cd on the integrity of the actin cytoskeleton of haemocytes are not directly linked to ROS production, at least at the exposure conditions used in the present study.

In vitro effects of cadmium on two different animal cell models.

The aim of this study was to assess comparatively the effects of cadmium on two different in vitro cell models, a cell line derived from proximal tubule renal cells (LLC-PK1) and haemocytes or blood cells of mussels (Mytilus galloprovincialis). Cells were seeded in 96-well microplates and exposed in vitro to different concentrations of cadmium (CdCl(2)) ranging from 10 to 2000 microM for haemocytes and from 1 to 100 microM for LLC-PK1 cells, added to the culture medium. After 24 h of exposure, different assays were performed on haemocytes: neutral red uptake, phagocytosis of neutral red-stained zymosan, XTT assay, activity of lysosomal acid phosphatase and demonstration of the actin cytoskeleton using TRITC-labeled phalloidin. Cell viability expressed as LC50 was 750 microM when using the neutral red assay and 400 microM with the XTT assay. The phagocytic ability and the activity of acid phosphatase increased significantly in cells treated with Cd in a non dose-dependent manner. Doses of Cd above 100 microM caused disruption of the actin cytoskeleton. In LLC-PK1 cells, cell viability expressed as LC50 was found to be around 40 microM when using the neutral red assay and 50-60 microM with MTT and LDH assays, respectively. These results show that mussel haemocytes are in general more resistant to Cd exposure than LLC-PK1 cells. Furthermore, Cd appears to stimulate phagocytic and lysosomal activities in haemocytes in vitro.

Tissue and cell distribution of copper, zinc and cadmium in the mussel, Mytilus galloprovincialis, determined by autometallography.

The localization of metals in selected tissues of metal-exposed mussels was investigated by means of autometallography. Mussels collected from a Zn-polluted site were (a) depurated or, alternatively, (b) exposed to either Cu, Zn or Cd for 41 d. Mussels collected from a clean site were used as experimental reference. Autometallographically demonstrated black silver deposits (BSD), indicating the presence of metals, were observed in gills, (a) in frontal cells and haemocytes of Cu-exposed mussels, (b) in secretory postlateral and abfrontal cells and in endothelial cells of Zn-exposed mussels, and (c) in frontal, postlateral and endothelial cells but mainly in abfrontal cells and haemocytes of Cd-exposed mussels. Autometallography also revealed the presence of BSD in connective tissue brown cells underlying the mantle. Additionally, adipogranular cells of the connective tissue surrounding the gonad follicles were positively stained but no BSD was found in gonad tissue. Scarce BSD were found in the cytoplasmic granules of the stomach wall of control mussels whilst depurating and metal-exposed mussels exhibited BSD lining the apex of the stomach epithelial cells. Contrary to the results previously obtained with marine gastropod molluscs, BSD were not found in the basal lamina of digestive tubules, stomach, and ducts of mussels. Highly conspicuous BSD were observed in digestive cell lysosomes of depurating and metal-exposed mussels. Basophilic cells were always devoid of BSD. Finally, BSD were also found in nephrocyte lysosomes and mineralized concretions.