Genotoxic and histopathological biomarkers for assessing the effects of magnetic exfoliated vermiculite and exfoliated vermiculite in Danio rerio
Graphical abstract
Introduction
Water quality is one of the largest challenges currently faced because clean water is indispensable for aquatic organisms and human health (Schwarzenbach et al., 2010) and is essential as a raw material in a variety of industries (Savage and Diallo, 2005, Pradeep, 2009). Among the anthropogenic sources of water and environmental pollution, oil spills have been of great concern worldwide. According to an Earth Gauge report (2010), beyond exterminating several species of sea dwellers, oil spills can also affect the health and the reproductive cycle of those that survive, resulting in irreversible damage to natural ecosystems. The remediation of oil spill accidents is a complex issue, and conventional technologies have not addressed the issue properly, particularly in the case of massive environmental contamination. However, in recent years, floating magnetic sorbents in the form of magnetic polymer foam and vermiculite/iron oxide nanocomposites have been successfully formulated (Da Silva et al., 2010).
Vermiculite has a lamellar form and consists of a hydrated silicate containing varying amounts of iron, magnesium, potassium, and aluminum. A key advantage of the vermiculite deposits found in Brazil is their asbestos-free composition (França and Ugarte, 2005). This mineral expands up to forty times when heated to temperatures approximating 1000 °C, yielding low-density flakes named exfoliated vermiculite (EV), which absorbs liquids by capillarity (Mysore et al., 2005, Da Silva et al., 2010). These characteristics allow the production of magnetic nanocomposites by using an aqueous colloidal suspension of magnetic nanoparticles (iron oxide nanoparticles) as a seeding material for encapsulation within vermiculite or to promote a magnetic coating of the vermiculite surface, thus generating a magnetic nanocomposite. Such a magnetic nanocomposite, named magnetic exfoliated vermiculite (MEV), was developed to absorb hazardous substances, such as oils spilled in natural water reservoirs. After absorption, the oil-based compounds can be retrieved from the water by magnetic separation, allowing both the recovery of the water reservoir plus the control and reduction of environmental pollution (Oliveira, 2008). Additionally, the magnetic nanocomposite can be recycled and reused, with a reduced rate of degradation in successive cycles. Despite these advantageous outcomes, it is necessary to assess the toxicological hazard and risks associated with exposure to this particular technology.
For environmental impact assessment, aquatic organisms such as Danio rerio are widely used as biological markers (Bolognesi et al., 2004, Ferraro et al., 2004, Ladhar et al., 2014) because they represent the highest trophic level of the food chain and are quite sensitive to environmental pollution (Ong et al., 2014), metabolizing and accumulating xenobiotics over time (Dautremepuits et al., 2004, Torres de Lemos et al., 2007, Domingues et al., 2010).
Although vermiculite being characterized and studied by its adsorption capacity for water spilled contaminants (Da Silva et al., 2003, Abate and Masini, 2007, Duman and Tunç, 2008, Zhao et al., 2011, Xue et al., 2014), there are no studies on its potential toxic effect on aquatic organisms. In 1995, an in vitro study was carried out for assessing toxic effects of vermiculite, using human polymorphonuclear leukocytes (PMN) and bovine alveolar macrophages (AM), finding that vermiculite has a moderate hemolytic activity and a high ability to elicit ROS production (Governa et al., 1995). In order to obtain new insights about the toxicological potential of exfoliated vermiculite (EV) and magnetic exfoliated vermiculite (MEV), in our study were evaluated the acute toxicological effects of these materials in D. rerio by using genotoxic and histopathological biomarkers, by assessing DNA fragmentation and by morphological alterations in the gills, liver, and intestine.
Section snippets
Synthesis and characterization of magnetic exfoliated vermiculite (MEV) and exfoliated vermiculite (EV)
The exfoliated vermiculite, the precursor of the nanocomposite, was supplied by Brasil Minérios (Brazil), and the magnetic nanocomposite was prepared according to the procedure described by de Oliveira (2008). Then, maghemite nanoparticles were prepared by the oxidation of magnetite nanoparticles, synthesized by the alkaline hydrolysis of iron ions, as described previously (Soler et al., 2011). The nanoparticles were dispersed in HCl aqueous solution following sonication, thus yielding a stable
Characterization of magnetic exfoliated vermiculite (MEV) and exfoliated vermiculite (EV)
The TEM analysis of isolated, iron oxide-based nanoparticles provided an average particle diameter of 10 ± 3 nm (Fig. 1). The particles appeared nearly spherical in shape and had a narrow diameter range.
The MEV (Fig. 2A) and EV samples (Fig. 2B) that were observed by SEM exhibited irregular structure, comprising stacked plates that were also arranged irregularly. The SEM analysis of the MEV also showed the presence of magnetic nanoparticles in clusters adsorbed onto the EV matrix (Fig. 2A). The
Discussion
Despite being a mineral broadly used, studied (adsorption capacity) and characterized (physicochemical) as adsorbent for water spilled contaminants (Da Silva et al., 2003, Abate and Masini, 2007, Duman and Tunç, 2008, Zhao et al., 2011, Xue et al., 2014), there are no studies on vermiculite's potential toxic effect on aquatic organisms. It is sold by several companies under the CAS number 1318-00-9 in different countries, where information on fact sheets generally show vermiculite has low or no
Conclusions
The information collected in this study suggests that the concentrations of the magnetic exfoliated vermiculite and exfoliated vermiculite tested do not cause significant histopathological or cytological alterations (the formation of MNs and NAs) in the gills, liver, intestine or erythrocytes of D. rerio. However, the DNA fragmentation caused by exposure to the magnetic exfoliated vermiculite is related to genotoxic but not mutagenic damage. In this sense the results obtained by comet assay can
Funding information
This study was supported by the Brazilian National Council for Scientific and Technological Development (CNPq).
Acknowledgements
The authors are grateful to the Brazilian National Council for Scientific and Technological Development (CNPq), the Brazilian Coordination for the Improvement of Higher Education Personnel (CAPES) and the Brazilian National Institute of Science and Technology in Nanobiotechnology (INCT in Nanobiotechnology).
References (57)
- et al.
Fish micronuclei for assessing genotoxicity in water
Mutat. Res.
(1995) - et al.
Investigation of micronuclei and other nuclear abnormalities in peripheral blood and kidney of marine fish treated with crude oil
Aquat. Toxicol.
(2006) - et al.
Comet and micronucleus assays in zebra mussel cells for genotoxicity assessment of surface drinking water treated with three different disinfectants
Sci. Total Environ.
(2004) - et al.
Adsorption of crude oil on anhydrous and hydrophobized vermiculite
J. Colloid Interface Sci.
(2003) - et al.
Magnetic characterization of vermiculite-based magnetic nanocomposites
J. Non-Cryst. Solids
(2010) - et al.
Humoral immune factors modulated by copper and chitosan in healthy or parasitised carp (Cyprinus carpio L.) by Ptychobothrium sp. (Cestoda)
Aquat. Toxicol.
(2004) - et al.
Biomarkers as a tool to assess effects of chromium (VI): comparison of responses in zebrafish early life stages and adults
Comp. Biochem. Physiol. C Toxicol. Pharmacol.
(2010) - et al.
Poly(d, l-lactide-co-glycolide)/montmorillonite nanoparticles for oral delivery of anticancer drugs
Biomaterials
(2005) - et al.
HUMN project: detailed description of the scoring criteria for the cytokinesis-block micronucleus assay using isolated human lymphocyte cultures
Mutat. Res.
(2003) - et al.
Formation of the digestive system in zebrafish
I. Liver morphogenesis. Dev Biol
(2003)
Oxidative stress responses in different organs of carp (Cyprinus carpio) with exposure to ZnO nanoparticles
Ecotoxicol. Environ. Saf.
Bleomycin-induced DNA damage and its removal in lymphocytes of breast cancer patients studied by comet assay
Mutat. Res.
The influence of engineered Fe(2)O(3) nanoparticles and soluble (FeCl(3)) iron on the developmental toxicity caused by CO(2)-induced seawater acidification
Environ. Pollut.
Developmental toxicity of Japanese medaka embryos by silver nanoparticles and released ions in the presence of humic acid
E. Environ. Pollut.
Application of the micronucleus and comet assays to mussel Dreissena polymorpha haemocytes for genotoxicity monitoring of freshwater environments
Aquat. Toxicol.
Effects of waterborne nano-iron on medaka (Oryzias latipes): antioxidant enzymatic activity, lipid peroxidation and histopathology
Ecotoxicol. Environ. Saf.
Do nanoparticles present ecotoxicological risks for the health of the aquatic environment?
Environ. Int.
Synthesis and characterization of size-controlled cobalt-ferrite-based ionic ferrofluids
J. Magn. Magn. Mater.
Treatment of oily waters using vermiculite
Water Res.
Noble metal nanoparticles for water purification: a critical review
Thin Solid Films
A simple technique for quantitation of low levels of DNA damage in individual cells
Exp. Cell Res.
Chemical analysis of size-tailored magnetic colloids using slurry nebulization in ICP-OES
Microchem. J.
Toxicity of potential antibacterial vermiculite material-preliminary study on an animal model
Int. J. Oral Maxillofac. Surg.
River water genotoxicity evaluation using micronucleus assay in fish erythrocytes
Ecotoxicol. Environ. Saf.
The micronucleus test in piscine erythrocytes
Aquat. Toxicol.
The micronucleus test in piscine erythrocytes
Aquat. Toxicol.
Improvement of oil adsorption performance by a sponge-like natural vermiculite-carbon nanotube hybrid
Appl. Clay Sci.
Secretion of intestinal goblet cells: a novel excretion pathway of nanoparticles
Nanomedicine
Cited by (11)
Copper II oxide nanoparticles (CuONPs) alter metabolic markers and swimming activity in zebra-fish (Danio rerio)
2022, Comparative Biochemistry and Physiology Part - C: Toxicology and PharmacologyMicronucleus test and nuclear abnormality assay in zebrafish (Danio rerio): Past, present, and future trends
2021, Environmental PollutionCitation Excerpt :It should be noted that most of the studies reviewed did not observe the NA formation in zebrafish after exposure to nanomaterials (Fig. 9). No mutagenic effects were observed in zebrafish after exposure to carbon nanotubes (Cimbaluk et al., 2018), carbon nanopowder (Della Torre et al., 2017), CuO NPs (Vicario-Parés et al., 2017), Au NPs (Ramachandran et al., 2018), fullerene C60 (Della Torre et al., 2018), poly (D, L-lactic-co-glycolic acid) nanospheres (Deepika et al., 2019), and magnetic exfoliated vermiculite nanocomposites (Cáceres-Vélez et al., 2016). Revised data showed that the mutagenic effects of nanomaterials in fish species are dependent on their physical, chemical, biological, mechanical, and electrical properties, such as reported for Ag NPs (30 nm; 15.5–31 μg L−1; 4–14 days) and Au NPs (200–500; 9.7–58.2 μg L−1; 4–14 days) in adult zebrafish.
Histopathological, genotoxic, and behavioral damages induced by manganese (II) in adult zebrafish
2020, ChemosphereCitation Excerpt :It may delay or decrease the MnCl2 elimination and increase its relative amount in plasma (Ballatori, 2000). Histopathological lesions in this organ have been studied by several authors as a way to evaluate the toxicity of different substances, due to its metabolizing function (Cáceres- Vélez et al., 2016; Souza et al., 2017). In other studies with zebrafish assessing toxicity of other substances, there are also reports of cell vacuolization as one of the most frequently encountered changes (Velasco- Santamaría et al., 2011; De Oliveira et al., 2015; Pereira et al., 2016).
Magnetite nanoparticles effects on adverse responses of aquatic and terrestrial animal models
2020, Journal of Hazardous MaterialsCitation Excerpt :Fish exposure to metal oxide nanoparticles affects multiple levels of biological organization such as developmental malformation of organs, gills and skin damage, abnormal behavior, immunotoxicity, genotoxicity or altered gene expression, neurotoxicity, endocrine system disruption, respiratory toxicity and finally mortality (Shaw and Handy, 2011; Chakraborty et al., 2016; Li et al., 2009; Handy et al., 2011; Zhu et al., 2012; Piccinetti et al., 2014). Specifically, zebrafish Danio rerio has been extensively used in toxicity bioassays (Shaw and Handy, 2011; Zhu et al., 2012; Xiong et al., 2011), indicating species sensitivity to environmental pollution (Domingues et al., 2010; Cáceres-Vélez et al., 2016). On the contrary, little research has been performed with other finfish species, as the prussian carp Carassius gibelio, a freshwater species that is widely distributed in European and Asian inland waters (Froese and Pauly, 2019).
Impact of humic acid on the persistence, biological fate and toxicity of silver nanoparticles: A study in adult zebrafish
2019, Environmental Nanotechnology, Monitoring and ManagementCitation Excerpt :For all the in vivo tests, blind analysis was used in order to avoid the biasing of the results until the analysis was completed. Peripheral erythrocytes of zebrafish were used to detect the DNA damage caused by exposure to AgNPs, with or without HA, using the alkaline comet assay, and nuclear abnormalities and micronucleus test, according to a published protocol (Kosmehl et al., 2008; Cáceres-Vélez et al., 2016). Blood samples were collected and placed in 500 μL of fetal bovine serum to obtain a single-cell suspension per fish.
Comprehensive Toxicity Assessment of PEGylated Magnetic Nanoparticles for in vivo applications
2019, Colloids and Surfaces B: Biointerfaces