Monaco, Capriello, Grimaldi, Schiano, and Ferrandino: Neurodegeneration in zebrafish embryos and adults after cadmium exposure

Neurodegeneration in zebrafish embryos and adults after cadmium exposure





Abstract

Cadmium is a biologically non-essential metal. It is also toxic to many organs including the brain. The aim of this study was to analyse the neurodegenerative effects of this metal in embryos and adults of zebrafish exposed to sub-lethal concentrations of cadmium. The study was performed by cytochemical stainings. Six hours post fertilisation (hpf) zebrafish embryos were treated for 24 hours with 9 μM of cadmium and subsequently stained with Acridine orange in whole mount to detect apoptosis in the brain. Adult zebrafish were treated for 16 days with the same concentration of cadmium, and cell death in the brain was detected by Fluoro- Jade B staining at 2, 7 and 16 days of treatment. An increase in cell death was observed only at 16 days of treatment in adults, while an increase in apoptotic events was revealed in the brain of embryos after 24 h of treatment. This evidence is indicative that cadmium, even at a sub-lethal concentration, induces cell death in the brain of embryos but also in adults of zebrafish in which the phenomenon appears timedependent.

Introduction

Cells react to stress by activating different pathways. Among the reactions cell death can be triggered to eliminate damaged cells. It plays an important role both in its programmed forms and in pathological processes including diseases. Hence the field of cell death has attracted great interest in recent years, especially with respect to studying neurodegenerative diseases. Apoptosis, necrosis and autophagy are distinctive forms of cell death. Different biochemical signals start the process of cell death and action mechanisms depend on the cell’s ability to cope with the conditions to which it is exposed.1 In the nervous tissue such conditions may include the lack of neurotrophic factors,2 excitotoxicity,3 oxidative stress due to reactive oxygen species (ROS), and alteration of calcium signalling4 but also exposure to toxic insults such as metals.5

Cadmium (Cd) is a non-essential metal for the human metabolism at any concentration. Unfortunately, it has a high environmental impact and a long biological halflife of ~30 years with several effects on different organs, inducing apoptosis in vitro and in vivo.6 In recent years it has also been indicated as a possible aetiological factor in neurodegenerative diseases.7 Cd significantly increases the levels of lipid peroxidation8 and induces accumulation of ROS, which leads to oxidative stress.9 Cd also breaks homeostasis of intracellular free calcium (Ca2+), an ion that acts as a signalling mediator in numerous cellular processes including cell proliferation, differentiation and survival/death. Although Cd appears to exert its action through the stimulation of defence processes such as activated metallothionein and chaperones,10 numerous studies in vitro and in vivo have shown its ability to induce apoptosis and autophagy in different animal models.6,11,12 Indeed, Cd induces cell death in liver,13 in kidney cells,14 in muscle15 and in the brain of teleost fish16 but also in reptiles.17

We previously demonstrated that Cd accumulates in the zebrafish brain with consequent mitochondrial damage and vacuoles observed in this organ under transmission electron microscopy.18 Mitochondrial damage is a well-known triggering factor of cell death. Recently we also showed the ability of this metal to damage glial cells,19 essential for proper brain homeostasis. In the present work, our aim was therefore to investigate cadmium’s ability to induce neurodegeneration both in the brain of zebrafish adult specimens treated for 16 days and in embryos after 24 h of exposure, in both cases to 9 μM of Cd.

Materials and Methods

Animals

Specimens of adult zebrafish were housed in well-oxygenated tanks, with a natural photoperiod of 12 h:12 h light/dark, at a temperature of 28.5°C and a pH of 7.6. The fish were fed twice a day with Tetra- Min, and water parameters and quality were checked daily throughout the experiment. 20,21 All the experiments were performed in accordance with the Guidelines for Animal Experimentation of the Italian Department of Health.

Embryo breeding

Embryos were generated from the above fish, collected with a siphon from the fish tanks and housed in Petri dishes with E3 medium (5 mM NaCl, 0.17 mM KCl, 0.33 mM CaCl2 .2H2O, 0.33 mM MgSO4), kept in a water bath at 28.5°C. At 6 h postfertilisation (hpf), the fertilised eggs were selected and then used for experimental procedures.

Embryo treatment

Healthy embryos at 6 hpf were selected with a Leica Zoom 2000 stereomicroscope at 10x magnification and were exposed to the metal for 24 h. For the acute treatment in vivo, a stock solution of 50 mM CdCl2 (Carlo Erba, Cornaredo, MI, Italy) was prepared by dissolving 2.51 g of salt in 250 mL of breeding solution, and serial dilutions were used to prepare the work solution with 9 μM of Cd concentration. We used a total of 90 treated embryos plus 90 controls simply exposed to breeding solution (resulting from a triplicate treatment). The treatments were conducted in multi-well plates (10 embryos per well) incubated at 28.5°C.

Acridine orange staining in whole Mount

Apoptosis can be visualised in wholemount of embryos or tissues using dyes such as Acridine orange.22 Apoptosis was analysed in whole-mount embryos with an exposure to the sub-lethal concentration of 9 μM, starting from 6 hpf and for 24 h. Control and treated embryos were placed in clean vials. Several rinses were performed with breeding solution to remove the precipitated salts and residues of Cd in the solution of the treated embryos. The embryos were then exposed to a solution of Acridine orange (Carlo Erba) at a concentration of 100 μg/mL for 1 h, after which several rinses were performed to remove the excess dye. The embryos were then mounted in a drop slide with glycerol and PBS. The images were acquired with a Kontron Electronic Imaging System KS300 (Zeiss, Oberkochen, Germany) by setting the FITC channel. Apoptotic cells were quantified by counting all fluorescent cells in embryo brains using the cell count tool of ImageJ software.

Breeding and treatment of adult fish with cadmium chloride

Adult specimens of zebrafish from 4 to 10 months of age were used to evaluate Cd toxicity. The fish were housed and acclimated in tanks equipped with their own oxygenator and thermostat at a temperature of 28.5°C, with natural photoperiod, and fed with commercial food. The fish were divided into two pools: a control pool with twelve fish exposed to uncontaminated water and one in which twelve fish were exposed to 9 μM of Cd for 16 days. The tanks underwent water and CdCl2 replacement on a daily basis. We assessed the progress of the damage after 2, 7 and 16 days from the beginning of the treatment. Fish were sacrificed by an overdose of MS- 222.19,23 The brains were rapidly extracted and fixed in Bouin solution for 24 h, subsequently dehydrated and embedded in paraffin.

Histochemical staining by Fluoro- Jade B

Fluoro-Jade B (AG310 EMD, Millipore, Billerica, MA, USA) is an anionic fluorochrome derived from fluorescein. It is commonly used in neuroscience to reveal degeneration of neurons in the central nervous system resulting from exposure to a variety of neurotoxic insults.24 Six-μm thick brain sections were deparaffinized and rehydrated in absolute ethanol for 3 min, then in 70% ethanol for 1 min and finally in distilled water. Subsequently, the sections were incubated for 1 h at 4°C with Fluoro- Jade B, gently shaken in the dark with an orbital shaker. Then the slides were dried overnight at room temperature. The next day the sections were clarified and mounted. The fluorescence images were acquired with a Kontron Electronic Imaging System KS300 (Zeiss) by setting the FITC channel. Analysis of cellular reactivity was performed by comparing the number of fluorescent cells, counted by ImageJ software, in 0.1 mm2 of brain tissue.

Graphics preparation and statistical Analysis

Graphics and statistical analysis were processed by GraphPad Prism 5 (Graph-Pad Software, Inc., La Jolla, CA, USA). Student’s t-test was used to evaluate the difference of Acridine orange fluorescence between control and treated specimens, while to evaluate the differences of Fluoro- Jade B staining the one-way ANOVA test with Tukey’s post-hoc test (P=0.05) was used. Data are mean ±SD: P<0.05 was considered to be statistically significant (*) and P<0.001 very significant (***).

Results

Acridine orange staining

Control and treated embryos at 30 hpf with a regular phenotype were used for the study of apoptosis in brain of whole mount. An increase in fluorescent cells was observed in treated embryos with respect to controls for all brain areas (Figure 1 a,b). From a count of positive cells in the brains of 50 embryos for the experimental group, a 3-fold increase in the number of apoptotic cells was observed in brains of embryos exposed to Cd compared with the controls (Figure 2). Interestingly, there was an increase in the number of fluorescent cells in all brain areas.

Fluoro-Jade B staining

Application of the histochemical technique by Fluoro-Jade B to detect possible degenerative phenomena was able to identify different fluorescent signals in control and treated adult fish. Few fluorescent signals were revealed in control brains, like those shown in treated fish at 2 and 7 days as reported in the graph for the telencephalon, diencephalon and midbrain (Figure 3). In fish brains at 16 days of treatment a diffused fluorescent signal was revealed especially in the same areas (Figures 3 and 4). In the telencephalon of these fish we observed 55±10 positive cells/0.1 mm2 against 11±5 positive cells/0.1 mm2 present in the control. The diencephalon appeared to be the area with more positivity than others: Fluoro-Jade B (+) cells in diencephalon numbered 69±4 cells/0.1 mm2 vs 10±3cells/0.1 mm2 for the control. In the midbrain we observed 60±11cells/0.1 mm2 vs 13±6 cells/0.1 mm2 for the control. The morphology of positive cells appeared variable and probably relative to different cellular types, neurons and also glial cells. Furthermore, fluorescence was particularly present at the level of cell bodies and few nervous processes were stained (Figure 4).

Discussion

These data confirm the ability of Cd to damage the brain of adult animals and induce alterations in the processes of nervous system development, as was previously observed in other studies.25,19,10 In particular, this work shows that Cd induces death of nervous cells both in embryos and in the encephalon of adult fish. Since the concentration able to induce cytotoxicity is characteristic of contaminated environments, our findings are of ecotoxicological importance. In previous reports, we observed that zebrafish exposure to Cd at a rate concentration of 1 mg/L for 16 days caused alterations in the neuroglial component of the zebrafish brain already after 2 days of treatment. 19 Some of these alterations could be the cause or effect of cell death, as we hypothesised. Consistent with this hypothesis were also observations made by similar experiments on the same model18 where alterations were observed in mitochondrial morphology, a principal feature of cell death mechanisms and degeneration processes.

Fluoro-Jade B is widely used in the field of neuropathology and in animal models of neurological disorders.26 This dye is able to evidence degeneration phenomena of nerve cells with a positivity both for neurons and glial cells,27,28 considering different types of cell death such as apoptosis and necrosis.29 Interestingly, we observed that Fluoro-Jade B positivity significantly increased only after 16 days of exposure to Cd, and the area that showed a marked increased signal was the diencephalon. Other positive cells were also observed in the telencephalon and midbrain. Such observations indicate that cell death also in zebrafish brain cells is a mechanism induced by Cd and that not all brain areas respond in the same way, perhaps due to the differing sensitivity to Cd of the various cell populations which are present in the different areas of the zebrafish brain. For example, it has long been known that certain brain cell types, such as dopaminergic neurons, are more susceptible to oxidative stress and environmental stressors and they are affected in several neurological disorders caused by the reduction in functionality of clearance and detoxification processes considering susceptibility to modified and oxidized proteins like alpha synuclein.30 However, further investigations are needed to elucidate the cell death processes induced by Cd in the zebrafish brain since there are known to be several different ways in which this metal can affect brain cells.

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Figure 1.

Acridine orange stain in whole-mount zebrafish embryos. a) Control embryos. b) Embryos after 24-hour treatment; note an increase in the number of fluorescent cells in all brain areas. fb, forebrain; mb, midbrain; hb, hindbrain. Scale bar: 75 µm.

ejh-61-4-2833-g001.jpg
Figure 2.

Average of the positive fluorescent cells in the embryos after 24-hour treatment with 9 µM of Cd and in the control embryos by Acridine orange staining in whole-mount. A 3-fold increase in apoptotic cells was observed in the treated embryos compared with the controls. *P>0.05.

ejh-61-4-2833-g002.jpg
Figure 3.

Graphical representation of the mean numbers of Fluoro-Jade B positive cells/0.1 mm2 in the area of the telencephalon, diencephalon and midbrain in zebrafish adults after 2, 7 and 16 days of treatment with 9 µM of Cd and in control fish. Fish treated at 2 and 7 days showed few fluorescent signals similar to those revealed in control brains. A diffused fluorescent signal was particularly revealed at 16 days of treatment and the diencephalon appeared to be the area with more positivity than the others. ***P>0.001.

ejh-61-4-2833-g003.jpg
Figure 4.

Fluoro-Jade B staining. Sagittal sections: a) telencephalon, b) diencephalon and c) midbrain in control adult fish; d) telencephalon, e) diencephalon and f ) midbrain of adults after 16 days treated with 9 µM of Cd. Note the increase in fluorescence in treated fish compared with the control. Fluorescence was especially present at the level of cell bodies and few nervous processes were stained. Scale bar: 50 µm.

ejh-61-4-2833-g004.jpg
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Copyright (c) 2017 Antonio Monaco, Teresa Capriello, Maria C. Grimaldi, Valentina Schiano, Ida Ferrandino

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