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Sludge from Wastewater treatment plants (WWTPs) have been determined as a sink of microplastics (MP) removed from wastewater. The aim of this research work has been to evaluate the presence of these pollutants in the sludge of seven WWTPs (five urban and two industrial), located in southern Spain. Samples were collected in the primary, secondary and digested sludge matrixes, MPs were extracted following wet peroxide oxidation and the removal of cellulose, finally the samples were analyzed according to their abundance, size (from 100 µm to 5 mm), shape, colour, and polymer type. Subsequently, the data obtained on the WWTPs were compared, the main difference among the WWTPs and different sample points showed high heterogeneity in terms of abundance of microplastics, due to the differences in the sludge loaded, the processes and the type of sludge. The results from this study established that the most abundant shape was fibers; regarding the size, 100-355 µm fraction was the most abundant, showing that the amount of MPs increased when the size decreased. Regarding the type of polymers, 23 were identified by ATR-FTIR. Further, Acrylate, PE, EAA and PP were the most abundant found polymers. The presence of MPs in the digested sludge varied from 0.02 ± 0.006 MP g DW-1 to 57.18 ± 20.69 MP g DW-1 in the WWTP 6 (food industry) and WWTP 3 (urban city over 212,000 inhabitants), respectively; higher abundance of MPs found in the primary sludge in respect to secondary sludge; in concordance with the removal from wastewater line reported in other studies. The results obtained showed that MPs were widely present in sludge, becoming a sink of these pollutants, estimating that among 8.05 · 104 and 1.77 · 109 MPs · day-1 were loaded to sludge; therefore, these facilities act as a significant source of MPs into agriculture when sludge is used as soil amendment.

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The adsorption of molecules usually increases capacity and/or strength with the doping of surfaces with transition metals; furthermore, carbon nanostructures, i.e., graphene, carbon nanotubes, fullerenes, graphdiyne, etc., have a large specific area for gas adsorption. This review focuses on the reports (experimental or theoretical) of systems using these structures decorated with transition metals for mainly pollutant molecules' adsorption. Furthermore, we aim to present the expanding application of nanomaterials on environmental problems, mainly over the last 10 years. We found a wide range of pollutant molecules investigated for adsorption in carbon nanostructures, including greenhouse gases, anticancer drugs, and chemical warfare agents, among many more.

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The characterization of cholinesterase activity in brain and muscle of gilthead seabream was carried out using four specific substrates and three selective inhibitors. In addition, K m and V max were calculated from the Michaelis-Menten equation for ASCh and BSCh substrates. Finally, the in vitro sensitivity of brain and muscle cholinesterases to three organophosphates (OPs) was also investigated by estimating inhibition kinetics. The results indicate that AChE is the enzyme present in the brain, whereas in muscle, a typical AChE form is present along with an atypical form of BChE. Very low ChE activity was found in plasma with all substrates used. The inhibitory potency of the studied OPs on brain and muscle AChEs based on bimolecular inhibition constants (k i ) was: omethoate < dichlorvos < azinphosmethyl-oxon. Furthermore, muscle BChE was found to be several orders of magnitude (from 2 to 4) more sensitive than brain and muscle AChE inhibition by dichlorvos and omethoate.

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Using density functional theory (DFT) and molecular dynamics (MD), we studied the interaction of a titanium atom with a half of a C60 fullerene (i.e., C30), formed from the corannulene structure with a pentagonal base. We considered atmospheric pressure and 300 K. We found that the most stable adsorption of the titanium atom on C30 occurs in the concave surface of the molecule. Afterward, we investigated the interaction of the system C30-titanium with carbon monoxide and carbon dioxide molecules, respectively. We found that each of these molecules is chemisorbed, with no dissociation. The value of the adsorption energy for the carbon monoxide molecule varies from -0.897 to -1.673 eV, and for the carbon dioxide molecule, it is between -1.065 and -1.274 eV. These values depend on the initial orientation of these molecules with respect to TiC30. Graphical Abstract The TiC30 system chemisorbs CO or CO2ᅟwith no dissociation at atmospheric pressure and 300K.

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This study compared for seabream, Sparus aurata exposed to benzo(a)pyrene-B(a)P-, the response of molecular cytochrome P450 1A (CYP1A) and cellular histopathology biomarkers. Male gilthead seabream, Sparus aurata specimens were exposed for 20 days via water to a series of high B(a)P concentrations. CYP1A was assessed by measuring enzymatic activity (EROD) and CYP1A protein content, and cellular responses were evaluated by routine histopathological methods. In addition, biliary metabolites were measured in order to verify that B(a)P was absorbed and metabolised. Histological lesions, both in liver and gills, increased in parallel to B(a)P concentrations, with the majority of changes representing rather non-specific alterations. Hepatic EROD and CYP1A proteins data showed a concentration-dependent induction, while in the gills, EROD activity but not CYP1A proteins showed a non-monotonous dose response, with a maximum induction level at 200 microg B(a)P.L-1 and decreasing levels thereafter. The findings provide evidence that short-term, high dose exposure of fish can result in significant uptake and metabolism of the lipophilic B(a)P, and in pronounced pathological damage of absorptive epithelia and internal organs.

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An histological and histochemical study was conducted on the stomach of adult Senegal sole, Solea senegalensis specimens. The stomach was made up of four distinct layers: mucosa, lamina propria-submucosa-, muscularis and serosa. Surface epithelial, glandular and rodlet cells were present in the mucosa. Cells of the columnar epithelium contained a basal nucleus. Numerous mitochondria, granular endoplasmic reticulum and Golgi apparatus consisting of several parallel cisternae and vesicles were observed in the cytoplasm of these cells. The lysosomes were small, round and dense. The gastric glands were numerous in the pyloric and fundic regions but absent in the cardiac stomach. These glands were formed by two cell-types: light and dark cells. The light cells were characterised by numerous mitochondria, while dark cells had slightly fewer mitochondria and a tubulo-vesicular system. Rodlet cells similar to those observed in other teleostean fish were present among the epithelial cells. Although the epithelial cells of the mucosa contained a weak presence of neutral and acid mucopolysaccharides/mucosubstances, these substances were abundant in the lamina propria-submucosa. Proteins rich in arginine, lysine, cysteine and cystine were rarely present in the mucosa and lamina propria-submucosa of stomach, while proteins rich in tyrosine were abundant in these layers. Acid phosphatase, and ATP-ase (pH 7.2 and 9.4) activities were detected in the mucosa and lamina propria-submucosa. Alkaline phosphatase activity was not detected.

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A histological and histochemical study was performed in the buccal cavity and papillae, which were around the teeth, as well as in the oesophagus and oesogaster of the Senegal sole, Solea senegalensis adult specimens. The oesophagus and oesogaster were made up of four distinct layers: mucosa, submucosa, muscular and serous. Two morphological types of epithelial cells were distinguishable in the oesophageal mucosa: the more numerous type cells possessed an electron-dense cytoplasm, whereas the cytoplasm was electron-clear in the other cells. Mucus-secreting cells were the dominant feature of the epithelium throughout the oesophagus. These goblet cells were filled with numerous mucous droplets of low electron-density. The oesophagus was devoid of taste buds. In the oesogaster mucosa, three types of cells were distinguished: dark, rodlet and light epithelial cells. Dark epithelial cells showed different characteristics from that in the oesophagus: the nucleus was irregular with an electron-dense hyaloplasm, the cytoplasm had a scarce smooth and granular endoplasmic reticulum; a Golgi apparatus consisted of four parallel cisternae, dense granules without membrane, lysosomes and numerous mitochondria. The rodlet cells were elongated, contained rod-like structures and were surrounded by an electron-dense capsule-like structure. The bulk of the rodlet cell was composed of up to 20 extended rodlet units. Light epithelial cells of the oesogaster had the same characteristics as those observed in the oesophagus and contained numerous mitochondria with a dense matrix, abundant smooth endoplasmic reticulum and numerous vesicles. In the goblet cells of the papillae, sulfomucin was recognised, since they showed alcianophilia (alcian blue pH 1.0 and 0.5). These cells were negative to protein reaction (bromophenol blue) and contained -S-S- and SH groups. Enzymatic activities (alkaline phosphatase, acid phosphatase, ATPase (pH 7.2 and 9.4) and lipid reactions were negative in the goblet cells of the buccal cavity. Epithelial cells of oesophagus contained a weak presence of acid and neutral mucopolysaccharides. Oesophageal goblet cells contained carboxylated, sulphated (weakly and strongly ionised) mucosubstances and sialic acid. Most goblet cells did not contain proteins and presented disulphide (-S-S-) and sulphydril (-SH) groups. Proteins in general, and in particular those rich in lysine, tyrosine and arginine were present in the epithelium, lamina propria, submucosa and muscular layer of the oesophagus. Lipids in general and phospholipids were observed in the oesophageal epithelium while unsaturated, acid and neutral lipids were not observed. The lamina propria and submucosa contained a weak presence of phospholipids and unsaturated lipids. Acid phosphatase and ATPase (pH 7.2) activities were observed in the lamina propria, submucosa and muscular regions, while ATPase (pH 9.2) activity was weak in these areas. ATPase activity (pH 7.2 and 9.5) was very weak in the epithelium. Oesophageal goblet cells were negative to lipid and enzymatic reactions.

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The toxicity of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) has been demonstrated in the seabream Sparus aurata specimens. Liver presented hepatocytic alterations, with an increase of lipid droplets and glycogen granules. Ultrastructural modifications of hepatocytes included RER fractionation, glycogen augmentation, as well as a rise in the number of lipid droplets, vacuoles and secondary lysosomes. In the gills, secondary lamellar epithelium showed hyperplasia, hypertrophy and lamellar fusion on the edge of the filaments. At the end of the exposure period (1 pg1(-1) TCDD for 20 days), some organelles in epithelial cells of the secondary lamellae and the tubular system of the chloride cells appeared altered. In the liver of TCDD-exposed specimens, immunoreactive cytochrome P-450 1A was concentrated close to the cytoplasmic and nuclear membranes, and positive granules were also evident throughout cytoplasm of the hepatocytes. Significant cytochrome P-450 staining was especially evident in endothelium of the hepatic vascular system. At the beginning of the exposure (1 pg 1(-1) TCDD, for 5 and 10 days), cytochrome P-450 immunostaining was observed in the cytoplasm of scarce hepatic cells and after 20 days of treatment, specific immunostained cytoplasmic granules were detected in most hepatocytes. In gills of TCDD-treated specimens, pillar-endothelial cells showed a cytochrome P-450 1A immunostaining concentrated close to the base of gill filaments and dispersed through the gill lamellae. There was also significant cytochrome staining of the endothelium of the branchial vascular system. However, no cytochrome immunoreactivity was observed in epithelial-respiratory cells.

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Senegales sole, Solea senegalensis, adult specimens were subjected to sublethal copper exposure (100 microg SO(4)Cu/L) for 7 days (contamination period) and afterward kept for 4 days without copper exposure (depuration period). In contaminated and detoxified specimens, the hepatocytes indicated a great number of lipid droplets compared to the control specimens. Some ultrastructural alterations such as partial disruption of the microvilli and endothelial lining of the sinusoids were observed in the hepatocytes. Lifting and swelling of the lamellar epithelium were common lesions in S. senegalensis gills due to the copper exposure. On the other hand, in contaminated and detoxified specimens, gills demonstrated separation of respiratory epithelium; chloride and pavement cells were also altered. Copper levels in gills, and especially in liver, increased during sublethal copper exposure (up to 7 days). During the detoxification period, Cu concentrations in gills and liver experienced variable changes. The results of the study indicate that histology is a successful tool capable of revealing sensitively and selectively even the sublethal effects of heavy metals on the environment and aquatic biota.

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Histochemical distribution and quantification of trace metals (copper-Cu-, zinc-Zn- and iron-Fe-) were studied in oyster, Crassostrea angulata heart (auricle and ventricle) from different southwest Spanish coasts. In green Crassostrea angulata specimens (green coloration in gills and visceral mass), numerous brown cells (blackish-brown) were observed in the wall of the auricles and dispersed by connective tissue, where inflammatory lesions related with granular amoebocytes were observed. However, only a few brown cells (translucent ligh-brown) were detected in auricles of normal oysters. Histochemically, Fe, Cu and Zn granules were observed in the wall of the heart (auricles), in brown cells, as well as in the granular amoebocytes, which are increased in green Crassostrea specimens. Auricle brown cells reacted weakly with PAS and Alcian Blue techniques. These cells contain proteins, as well as cysteine and cystine groups; these residues (-SH and S-S) being very abundant in the heart of green specimens, specially in brown cells and in granular amoebocytes. Lipofuscin granules were detected in these brown cells and in granular amoebocytes. On the other hand, in the heart (normal and green specimens), Zn levels were higher than Fe and Cu concentrations and heavy metals analyzed were lower in heart of normal than in green specimens. In green specimens, Cu and Zn levels were higher in auricles than in ventricles.

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Histochemical distribution of glycoproteins, carbohydrates and proteins rich in different amino acids were studied using histological and histochemical procedures, in Senegal sole, Solea senegalensis (Kaup, 1858) larvae from hatching until day 15. Glycogen, proteins and glycoproteins were detected in the yolk-sac of the larvae at hatching and during the yolk-resorption. The epithelial digestive system (brush border, enterocytes and goblet cells) contained neutral and acid mucins (carboxylated and/or sulphated). Glycogen was observed in the cytoplasm of the digestive absortive cells (enterocytes) and in the liver (hepatocytes) on day 3-4 posthatching. Protein reactions, and specially those that showed proteins rich in arginine, tyrosine and tryptophan, were very intense in the zymogen granules of the pancreatic cells. Oesophageal and intestinal goblet cells contained glucose N-acetyl and sialic acid residues, but the mucin content of these mucous cells did not show affinity towards Con-A, suggesting the absence of glycoproteins with Mannose and/or glucose residues. WGA showed a very intense positivity in the microvilli of the digestive epithelium of the larvae and positive granules for both lectins, specially for Con-A, were detected in the cytoplasm of the anterior intestinal enterocytes.

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