Microscopy as a tool in toxicological evaluations · useful in toxicology, a relatively new field...
-
Upload
hoanghuong -
Category
Documents
-
view
217 -
download
1
Transcript of Microscopy as a tool in toxicological evaluations · useful in toxicology, a relatively new field...
Microscopy as a tool in toxicological evaluations
C.S. Fontanetti, C.A. Christofoletti, T.G. Pinheiro, T.S. Souza and J. Pedro-Escher
Instituto de Biociências, UNESP- Univ Estadual Paulista, Campus de Rio Claro, Departamento de Biologia, Laboratório
de Mutagênese, Av. 24A 1515, 13506-900 Rio Claro, São Paulo, Brasil.
The microscope was created to satisfy our interest in observing objects and/or structures under higher magnification. Both
the physical structure of the microscope and the techniques used for microscopic observation in the various fields of
science have undergone great technological changes since the device was first invented. Microscopy has been particularly
useful in toxicology, a relatively new field within the Biological sciences that studies the impacts of environmental
pollution on the different levels of biological organization. In this chapter, we demonstrate the many different ways in
which microscopy can be used in ecotoxicological studies to evaluate the impact of toxic substances on bioindicator
organisms. In this context, light microscopy aids in the identification of chromosomal aberrations, micronuclei, nuclear
abnormalities and histopathological alterations caused by exposure to chemical contamination; fluorescence microscopy can help detect whether a contaminant has genotoxic and/or mutagenic effects by revealing DNA damage; electron
microscopy enables the observation of alterations in the ultra-structure of the cell. Collectively, the different microscopy
techniques can contribute to the evaluation of the toxic, cytotoxic, genotoxic and mutagenic potential of pollutants, and
provide tools for a better understanding of the issue of contamination.
Key words: bioindicators; genotoxicity; histopathology; mutagenesis; pollutant; toxicity; ultrastructure.
Introduction
The microscope was created to satisfy our interest in observing objects under higher magnification, and later, to study
the morphology and function of cell structures and organelles, among other things. The first lens with magnifying
power, known as Lanyard Lens, was made from rock crystal and is datable to 721 a.d. Despite controversies
surrounding who actually created the first microscope, credit is usually given to Zacharias Jansen, from Holland, around
the year 1595. The device contained two superimposed lenses. Centuries later, Antonie van Leeuweenhoek (1632-1723)
and Robert Hooke (1635-1703) pioneered the utilization of the microscope in the evaluation of biological materials.
Since then, great technological advances have been incorporated into the microscope. For example, the electron
microscope has scanning coils that capture images produced by an electron beam tracing over the object, as opposed to
the rock crystal lenses of the primordial microscopes that needed the sun as a light source. Advances such as these have
enabled the development of techniques that allow for refined histological and ultrastructural evaluations.
Ecotoxicology is a relatively new science that can be defined as the study of the effects of pollutants (physical,
chemical and biological) on living organisms and how the latter interact with their respective habitats. Moreover, it is
also concerned with transport mechanisms, distribution, transformation, interaction and the final fate of pollutants in the
different compartments of the environment. Therefore, ecotoxicological analyses allow scientists to evaluate the
damage caused to the different levels of biological organization of an ecosystem.
Organisms respond to pollutants mainly through biochemical, physiological, and behavioural alterations [1, 2]. The
use of microscopy has enabled researchers to include several additional parameters to evaluate toxicity on bioindicators
such as fish, earthworms, diplopods, insects, onion, fava beans, and bacteria, among others; their reactions to toxic
agents are as diverse as they are.
In this context, light microscopy helps in the identification of chromosomal aberrations, micronuclei, nuclear
abnormalities and histopathological alterations caused by exposure to a chemically altered environment; fluorescence
microscopy can help detect whether the contamination has genotoxic and/or mutagenic effects by revealing damage to
the DNA; electron microscopy allows for the observation of alterations in the cell ultra-structure.
Below we describe the main techniques employed by light and electron microscopy in ecotoxicological evaluations,
and mention some commonly observed effects on selected bioindicator organisms.
1. Light microscopy
1.1. Cytogenetic techniques
Meristematic cells of Allium cepa (onion) are an efficient cytogenetic tool in the analysis of chromosomal aberrations
caused by environmental pollution [3].
Microscopy: Science, Technology, Applications and Education A. Méndez-Vilas and J. Díaz (Eds.)
©FORMATEX 2010 1001
______________________________________________
The technique used to stain the roots of anion is the Feulgen reaction [4]. According to the authors, this
stoichiometric method has become the best known cytochemical procedure used in conventional, quantitative DNA
analyses.
After Feulgen reaction, the radicular meristemes are lightly crushed with the help of one drop of 2% acetic carmin;
under the light microscope, a series of morphologic and cytogenetic parameters can then be quantified, including root
morphology and growth, mitotic rate, micronuclei induction and abnormal metaphase, anaphase and telophase (see
review in [5]).
Molluscs and fish are also excellent experimental models in toxicological studies. These organisms are specially
recommended for genotoxicity studies for two reasons. First, their component cells are very responsive to genotoxic
agents, even in low concentrations; second, they are an important source of protein and other nutrients in the human
diet. Food is the most important way through which toxic substances reach humans, and fish have been recognized as an
important vehicle of contamination [6].
The blood of fish exposed to an environmental sample and/or contaminant can be tested in two basic ways: through
the micronucleus test, which detects nuclear abnormalities, or with the comet assay. In mollusks, the hemolymph and
gills can be used in these tests. Both techniques are advantageous because they do not require a karyotypic profile of the
organism being tested [7], and can be used on any cell population, proliferating or not (as with the comet assay).
The micronucleus test is a promising, fast and cheap technique for genotoxicological analyses [8-12]. Slides for the
visualization of micronuclei and nuclear abnormalities are prepared with blood swabs previously subjected to Feulgen
reaction. Abnormalities are then quantified under the light microscope (Figure 1).
Figure 1. Micronucleus and nuclear alterations in erythrocytes of Oreochromis niloticus (Pisces). (A) Micronucleated erythrocyte
(head of arrow) and blebbed nuclei (arrow); (B) Notched nuclei (arrow); (C) Blebbed nuclei (arrow); (D) Lobed nuclei (arrows)
(Photos: Anita Martins Fontes Del Guercio).
Microscopy: Science, Technology, Applications and Education A. Méndez-Vilas and J. Díaz (Eds.)
1002 ©FORMATEX 2010
______________________________________________
The comet assay allows for the detection of potentially pre-mutagenic lesions, such as DNA chain ruptures, alkali-
labile sites, DNA adducts, base changes, crossed DNA-DNA and DNA-protein links and incomplete DNA repair [13-
14] in proliferating or non-proliferating in vitro cells [15]. This technique, which can be used on any tissue, has been
applied with success to erytrocytes of various species of mollusks and fish [16, 12, 17]. DNA damage is assessed using
a visual classification method on individual cells. Damaged cells, called comets, present a particular DNA migration
pattern in electrophoresis, presenting a “tail”. The severity of the DNA damage can be accessed through the length of
the tail, which is composed of DNA fragments, and classified into the following categories: 0, 1, 2 and 3; zero
representing the lowest amount of damage.
The results of the comet test can be visualised under the light microscope, after silver nitrate staining, or under the
fluorescent scope, after ethidium bromide staining (Figure 2).
1. 2. Histological and histochemical techniques
Histological alterations are sensitive tools that can be used to detect the direct toxic effects of various compounds on
different organs; therefore, they are good environmental stressor markers [18].
The main techniques used in the detection of histopathological damage caused by toxic agents include the inclusion
of the sample of interest in historesin or paraffin, followed by coloration with hematoxilin and eosin; other stains can
also be used. Histochemical techniques are specifically for the detection and distribution of certain compounds that aid
in the investigation of physiological alterations.
In addition to genotoxic alterations, particularly in the erythrocytes, fish exposed to pollutants may also present
histopathological changes in different tissues and organs such as liver, kidney, spleen and gills [19-21]. In molluscs,
alterations are observed mainly on the gills [22-23].
Morphological alterations found in the gills of fish (Figure 3) and mollusks vary, depending on the stressor and on
the intensity of the toxic agent [19-24].
Morphological alterations detected in the tissues of diplopods, particularly in the midgut and fat body, can be used to
access soil toxicity [25-27].
Figure 2. Comet assay applied in erythrocytes of Oreochromis niloticus (Pisces). (A) Class 0; (B) Class 1; (C) Class 2; (D) Class 3
(Photos: Tatiana da Silva Souza).
Microscopy: Science, Technology, Applications and Education A. Méndez-Vilas and J. Díaz (Eds.)
©FORMATEX 2010 1003
______________________________________________
Figure 3. Histological sections of Oreochromis niloticus gills (Pisces) from non-impacted environment (A) and impacted
environment (B, C and D). In (B) it is noted aneurism; In (C), lamellar fusion and in (D) detachment of the respiratory epithelium
(From Biagini et al., 2009).
2. Electronic microscopy
Ultramorphological analyses can be used to detect various tissue alterations and help in the diagnosis of symptoms of
cell intoxication [28]. Both the scanning electron microscope (SEM) and the transmission electron microscope (TEM)
are useful in such evaluations. The SEM provides a tridimentional view of the cell surface. For SEM visualization,
samples are dehydrated with increasing concentrations of acetone, dissected and covered with a thin layer of gold. By
contrast, the TEM produces a bidimentional image of the interior of the cell by detecting differences in density between
the various parts of the sample. Sample preparation for TEM comprises inclusion in resine and microslicing (20 a 400
nm slices).
The TEM allows for the observation of alterations on the surface of structures which cannot be detected under the
light microscope. In fish, for example, it is possible to observe alterations in the filaments of the gills and pavement
cells that cover them (Figure 4) [24, 29].
Microscopy: Science, Technology, Applications and Education A. Méndez-Vilas and J. Díaz (Eds.)
1004 ©FORMATEX 2010
______________________________________________
The TEM allows the observation of alterations in the organization of the cell (Figure 5) such as a decrease in the
number of organelles, loss of citoplasmatic and nuclear integrity, among others [23, 25].
Figure 4. SEM micrographs of the gill of Oreochromis niloticus (Pisces) from non-impacted environment (A, C) and impacted
environment (B, D). In (A) the gill filaments (f) are narrower and the lamellae (l) are longer than in (B). In (C), pavement cells (pc)
covered with microridges (arrows) and in (D), pavement cells with considerable loss of microridges (arrows); cc=chroridre cells.
Photos: A,B-Frederico Biagini; C, D-Luciana Tendolini Brito.
Microscopy: Science, Technology, Applications and Education A. Méndez-Vilas and J. Díaz (Eds.)
©FORMATEX 2010 1005
______________________________________________
Figure 5. Electron micrographs of the gill filaments of Mytella falcata (Mollusca) from non- impacted (A, C) and impacted
environments (B, D). (A) Frontal cells; (B) note the strong presence of secretory cells (sc); (C) lateral cells; (D) note smaller and
more abundant mitochondria; c=cilia; bb=basal bodies; m=mitochondria; mv=microvilli; n=nucleus; rer=rough endoplasmic
reticulum; sr=skeletal rod. Scale bars = 5 mm (From David et al., 2008b).
The growing concern with the effects of environmental pollutants is reasonable, not only because pollution is
ubiquitous, but also because little is known about its effects on living organisms. Microscopy is an invaluable tool in the
interpretation of the parameters used to measure toxicity, and contributes to the establishment of measures that aim to
prevent or eliminate environmental contamination, a risk not only to ecosystems, but also to human health.
References
[1] Who (World Health Organization). International Program on Chemical Safety (IPCS). Environmental Health Criteria 155.
Biomarkers and Risk Assessment: Concepts and Principles. Geneva.1993.
[2] Bücker A, Carvalho W, Alves-Gomes JA. Avaliação da mutagênese e genotoxicidade em Eigenmannia virescens (Teleostei:
Gymnotiformes) expostos ao benzeno. Acta Amazônica. 2006;36:357-364.
[3] Kristen U. Use of higher plants as screens for toxicity assessment. Toxicology in vitro. 1997;11:181-191.
[4] Mello MLS, Vidal BC. A reação de Feulgen. Ciência e Cultura. 1978;30:665-676.
[5] Leme DM, Marin-Morales MA. Allium cepa test in environmental monitoring: a review on its application. Mutation Research.
2009;682:71-81.
[6] Al-Sabti K, Metcalfe C. Fish micronuclei for assessing genotoxicity in water. Mutation Research. 1995;343:121-135.
[7] Hayashi M, Ueda T, Uyeno K, Wada K, Kinae N, Saotome K, Tanaka N, Takai A, Sasaki YF, Asano N, Sofuni T, Ojima Y.
Development of genotoxicity assay systems that use aquatic organisms. Mutation Research . 1998;399:125-133.
[8] Heddle JA, Hite M, Jrkhart B, MacGregor JT, Salamone MF. The induction of micronuclei as a measure of genotoxicity.
Mutation Research. 1983;123:61-118.
[9] Souza TS, Fontanetti CS. Micronucleus test and observation of nuclear alterations in erythrocytes of Nile tilapia exposed to waters
affected by refinery effluent. Mutation Research. 2006;605:87-93.
[10] Christofoletti CA. Avaliação dos potenciais citotóxico, genotóxico e mutagênico das águas de um ambiente lêntico, por meio
dos sistemas-teste de Allium cepa e Oreochromis niloticus. 118f. Dissertação (Mestrado em Biologia Celular e Molecular)
Universidade Estadual Paulista, Rio Claro-SP, 2008. Available at:
http://www.dominiopublico.gov.br/pesquisa/DetalheObraForm.do?select_action=&co_obra=118067 . Accessed April 5, 2010.
Microscopy: Science, Technology, Applications and Education A. Méndez-Vilas and J. Díaz (Eds.)
1006 ©FORMATEX 2010
______________________________________________
[11] Hoshina MM, Angelis DF, Marin-Morales MA. Induction of micronucleus and nuclear alterations in fish (Oreochromis
niloticus) by a petroleum refinery effluent. Mutation Research. 2008;656:44-48.
[12] Ventura BC, Angelis DF, Marin-Morales MA. Mutagenic and genotoxic effects of the Atrazine herbicide in Oreochromis
niloticus (Perciformes, Cichlidae) detected by the micronuclei test and the comet assay. Pesticide Biochemistry and Physiology.
2008; 90: 42-51.
[13] Singh NP, McCoy MT, Tice RR, Scheider EL. A simple technique for quantification of low levels of DNA damage in individual
cells. Experimental Cell Research. 1988;175:184-191.
[14] Tice, RR. The single cell gel/ comet assay: a microgel electrophoretic technique for the detection of DNA damage and repair in
individual cells. In: Phillips DH, Venitt, S, eds. Environmental Mutagen. CIDADE, Bios Scientific Publishers; 1995:315-339.
[15] Monteith DK, Vanstone J. Comparison of the microgel electrophoresis assay and other assays for genotoxicity in the detection
of the DNA damage. Mutation Research. 1995; 345: 97-103.
[16] David JAO, Hoshina MM, Fontanetti CS. DNA damage in Mytella falcata (Mytiloida, Mytilidae) cells: a new tool for
biomonitoring studies in tropical estuarine ecosystems. Naturalia. 2008a;31:1-7.
[17] Christofoletti CA, David JAO, Fontanetti CS. Application of the comet assay in erythrocytes of Oreochromis niloticus (Pisces):
a methodological comparison. Genetics and Molecular Biology. 2009; 32:155-159.
[18] Schwaiger J, Wanke R, Adam S, Pawert M, Honnen W, Triebskorn R. The use of histopathological indicators to evaluate
contaminant-related stress in fish. Journal of Aquatic Ecosystem Stress and Recovery. 1997;6:75-86.
[19] Mallat J. Fish gill structural changes induced by toxicants and other irritants: A statistical review. Canadian Journal of Fisheries
and Aquatic Sciences. 1985;42:630-648.
[20] Bernet D, Schmidt H, Meier W, Burkhardt-Holm P, Wahli T. Histopathology in fish: proposal for a protocol to asses aquatic
pollution. Journal of Fish Diseases. 1999;22:25-34.
[21] Machado MR. Uso de brânquias de peixe como indicadores de qualidade das águas. Ciência, Biologia e Saúde. 1999;1:63-76.
[22] David JAO, Fontanetti CS. The Role of Mucus in Mytella falcata (Orbigny 1842) Gills from Polluted Environments. Water, Air
and Soil Pollution. 2009;203:261-266.
[23] David JAO, Salaroli RB, Fontanetti CS.The significance of changes in Mytella falcata (Orbigny, 1842) gill filaments chronically
exposed to polluted environments. Micron. 2008b;39:1293-1299.
[24] Biagini FR, David JAO, Fontanetti CS. The use of histological, histochemical and ultramorphological techniques to detect gill
alterations in Oreochromis niloticus reared in treated polluted waters. Micron. 2009;40:839-844.
[25] Godoy J, Fontanetti CS. Diplopods as bioindicators of soils: analysis of midgut of individuals maintained in substract containing
sewage sludge. Water, Air and Soil Pollution. 2009;X:1-10.
[26] Souza TS, Hencklein FA, Angelis DF, Gonçalves RA, Fontanetti CS. The Allium cepa bioassay to evaluate landfarming soil,
before and after the addition of rice hulls to accelerate organic pollutants biodegradation. Ecotoxicology and Environmental Safety.
2009;72:1363–1368.
[27] Nogarol LR, Fontanetti CS. Acute and subchronic exposure of diplopods to substrate containing sewage mud: Tissular responses
of the midgut. Micron. 2010;41:239-246.
[28] Kammenga JE, Dallinger R, Donker MH, Kohler HR, Simonsen V, Triebskorn R, Weeks JM. Biomarkers in terrestrial
invertebrates for ecotoxicological soil risks assessment. Reviews of Environmental Contamination & Toxicology. 2000;164:93-147.
[29] David JAO, Salaroli RB, Fontanetti CS.The significance of changes in Mytella falcata (Orbigny, 1842) gill filaments chronically
exposed to polluted environments. Micron. 2008c;39:1293-1299.
Microscopy: Science, Technology, Applications and Education A. Méndez-Vilas and J. Díaz (Eds.)
©FORMATEX 2010 1007
______________________________________________