A combined DNA-microarray and mechanism-specific toxicity approach with zebrafish embryos to investigate the pollution of river sediments
Highlights
► This study analyzes the usability of transcriptomics for the characterization of sediment extract toxicity. ► Altered gene expression was compared to data from established bioassays as well as to chemical analysis. ► Gene expression profiling could be documented as a useful tool for the investigation of sediment extracts. ► Only a limited number of altered gene expression could be explained by analytical chemistry or biological effects.
Introduction
Ecotoxicogenomics attempts to link ecotoxicological effects resulting from exposure to toxicants with changes in (specific) gene expression patterns on the assumption that the gene expression in animals is altered in consequence of toxicity, either as a direct or an indirect result of toxicant exposure [1]. The challenge faced by (eco)toxicologists is to define, under a given set of experimental conditions, the characteristic and specific patterns of gene expressions elicited by a toxicant or environmental sample with known or potential toxicity [2], [3]. In the future, such knowledge might be helpful for the development of simulation models to predict the toxic effects by linking molecular biomarkers with population level effects, and, eventually, to even predict the ecologic risk of novel chemicals [2], [3].
Correlations of expression patterns in multiple samples may help to identify differentially expressed genes that play a role in embryogenesis, tissue patterning, organ development, and other physiological processes [4]. The challenge is to discriminate alterations associated with chemical toxicity from changes that are related to other stressors within normal adaptive responses not associated with truly adverse effects in an individual cell, organ, or organism [5]. By careful selecting appropriate sets of genes, one single microarray experiment could possibly combine numerous biologically relevant endpoints, provided the relevance of altered gene expression for the intact organism is truly understood.
For virtually all regulatory applications, endpoints most commonly assessed in toxicity tests with fish are those that can be directly related to effects at the population level: survival, growth (generally during early life-stages), sex ratio, and reproductive success [6]. To some extent, this holds true for bioassays addressing genotoxic effects or measure gene alterations, e.g. the formation of DNA adducts, DNA strand breaks, loss and/or chemical modifications of DNA bases as well as cross-linking of DNA [7], [8]. During the past several decades, a multitude of in vitro techniques have been developed to measure toxicity like toxicant-induced DNA damage or mutagenicity [9], [10], [11], [12], [13], [14], [15], [16], [17]. These assays include the Ames test [9], the Syrian hamster embryo cell transformation assay [18], micronucleus assays [19], measurements of sister chromatid exchange [20], unscheduled DNA synthesis [21] or the single cell gel electrophoresis (comet assay) [16]. Fundamental to all of these methods is the fact that toxicity is often preceded by, and/or results in, alterations in gene expression, with changes in gene expression being potentially far more sensitive, characteristic, and measurable endpoints than the toxicity itself [1]. Therefore, Nuwaysir et al. [1] propose genome-wide gene expression patterns as a tool highly informative of toxicant exposure to complement the established methods described above.
Hamadeh and co-workers reported that chemical-specific patterns of altered gene expression can be identified by high-density microarray analyses of tissues from exposed rats [22]. Likewise, gene expression profile approaches, were successfully used to discriminate between different classes of genotoxins in mice [23] as well as between different endocrine-disrupting compounds in carp [24] and to reliably predict the identity of toxicants in zebrafish [25]. Nevertheless, the specificity, sensitivity, and quantitative capabilities of high throughput transcriptomics/gene expression analyses for environmental applications are still in the early stages of evaluation [26].
Zebrafish eggs and embryos are receiving increasing attention, and in Germany the so-called “fish egg assay” has been validated for use in standardized wastewater assessment [27]. A modified version was submitted as the “Fish embryo test” (FET) to the Organization for Economic Cooperation and Development (OECD) Working Program [28], since the FET could be shown to have an excellent correlation to the acute fish test [29]. Various recent investigations also documented the suitability of zebrafish embryos for microarray investigations [25], [30], [31], [32], [33], [34].
The present study aimed to identify changes in the gene expression of zebrafish embryos as a response to exposure to selected sediment samples from the Rhine River, Germany. Over decades, the Rhine River in Germany had been strongly polluted with industrial and municipal waste waters. In the meantime, however, regulatory measures have been taken, and a good chemical and ecological status has been claimed for the surface waters by the European Water Framework Directive until 2015. In contrast to surface waters, river sediments still contain records of particle bound deposits of toxicants that can be remobilized during flood events [35] and are, e.g. able to cause DNA strand breaks in fish cells after dissociation from these particles by Soxhlet extraction [36]. However, chemical analysis did not correlate well with the genotoxic potential and, thus, the main cause of the effect, if any, remains unclear. Therefore, there is a need for approaches allowing detailed insight into the mechanisms underlying toxic response of model systems at the level of gene expression. DNA microarray techniques might provide such insight by comparing expression patterns elicited by sediment exposure to those produced by known contaminants. The approach is based on a correlation of DNA microarray data with a set of biological assays (e.g., mortality, cytotoxicity, mutagenicity, genotoxicity) as well as with chemical analyses for selected compounds including heavy metals and polycyclic aromatic hydrocarbons.
Section snippets
Sample location and preparation
In total, 18 sediment samples were collected from 2 locations along the Higher Rhine (outlet of Lake Constance to Basel) and 7 locations along the Upper Rhine (Basel to Bingen). In order to differentiate between older and more recent or remobilized pollution, (1) near-surface sediment samples (0–5 cm depth) were collected using a Van-Veen gripper and (2) core samples were taken from each location by a sediment corer (up to 150 cm depth) [37]. Carbon contents of the sediments were 7.4 ± 1.8%; total
Chemical analysis
The chemical analysis revealed a complex, though moderate contamination of many sites with different heavy metals and organic pollutants such as polycyclic aromatic hydrocarbons (PAHs). Hexachlorobenzene (HCB), however, could be detected at elevated concentrations, dramatically exceeding proposed quality levels for sediments (see below). To identify substances of concern according to their sediment concentration, the PAH, HCB and heavy metal contents were calculated as percentage of a sediment
Conclusion and recommendations
This is one of the first studies analyzing the usability of transcriptomics for the characterization of sediment extract toxicity. Gene expression profiling could be documented as a useful tool for the investigation of complex contaminated environmental samples such as sediment extracts. Results indicate that potential classes of contaminants can be assigned to sediment extracts by the use of classical biomarker genes and by correlating expression analysis of known substances. However, only a
Acknowledgements
The authors acknowledge financial support by the German Federal Ministry of Education and Research (grants 02WU1053 and 02WU1054). The present study was part of the research funding priority DanTox (DanTox – a novel joint research project using zebrafish (Danio rerio) to identify specific toxicity and molecular modes of action of sediment-bound pollutants). Additional funding was given by the European commission IP ZF models (LSHG-CT/2003/503496). The authors would like to express their thanks
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Sediment toxicity assessment using zebrafish (Danio rerio) as a model system: Historical review, research gaps and trends
2021, Science of the Total EnvironmentCitation Excerpt :Alterations in the xenobiotic metabolism of zebrafish embryos exposed to PAHs containing fraction of sediment extracts from the Vering Kanal was reflected by an increased cyp1a1 activity, upregulated cyp1 gene expressions (cyp1a, cyp1b1, cyp1c1, and cyp1c2), as well as upregulated ahr2 expression (Bräunig et al., 2015). Indeed, sediment contaminated with dioxin-like compounds, PBDEs, PCBs, PCDDs, and HCB can also act as inducers of zebrafish cyp1a (Kosmehl et al., 2012; Boulanger et al., 2019; Dong et al., 2019; Viganò et al., 2020). As well as CYP1A1 have commonly been used as biomarkers for planar aromatic substance classes exposure (e.g., PAHs), so metallothioneins (MTs) have been used as biomarkers for trace metal exposure.
Alterations to embryonic development and teratogenic effects induced by a hospital effluent on Cyprinus carpio oocytes
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2018, Water ResearchCitation Excerpt :For instance, certain transcriptome profiles were identifiable in rats (Hamadeh et al., 2002), in zebrafish embryos (Yang et al., 2007), and in whole adult zebrafish (Lam et al., 2008) exposed to certain compounds. Moreover, transcriptomic profiling of fish, such as largescale suckers (Christiansen et al., 2014), fathead minnows (Sellin Jeffries et al., 2012), and zebrafish (Bluhm et al., 2014; Kosmehl et al., 2012), exposed to environmental samples with unknown chemical composition can reveal affected biology and provide information on the exposure conditions or presence of potential classes of contaminants. However, challenges still remain in distinguishing between responses induced by specific classes of contaminants and the more universal detoxification mechanisms (Bluhm et al., 2014).
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Thomas Kosmehl and Jens C. Otte contributed equally to the manuscript as shared first authors.