A combined DNA-microarray and mechanism-specific toxicity approach with zebrafish embryos to investigate the pollution of river sediments

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Abstract

The zebrafish embryo has repeatedly proved to be a useful model for the analysis of effects by environmental toxicants. This proof-of-concept study was performed to investigate if an approach combining mechanism-specific bioassays with microarray techniques can obtain more in-depth insights into the ecotoxicity of complex pollutant mixtures as present, e.g., in sediment extracts. For this end, altered gene expression was compared to data from established bioassays as well as to results from chemical analysis. Mechanism-specific biotests indicated a defined hazard potential of the sediment extracts, and microarray analysis revealed several classes of significantly regulated genes which could be related to the hazard potential. Results indicate that potential classes of contaminants can be assigned to sediment extracts by both classical biomarker genes and corresponding expression profile analyses of known substances. However, it is difficult to distinguish between specific responses and more universal detoxification of the organism.

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

References (87)

  • J.G. Brewen et al.

    The effect of triated thymidine on sister chromatid exchange in a ring chromosome

    Mutat Res

    (1969)
  • T. Hu et al.

    Identification of a gene expression profile that discriminates indirect-acting genotoxins from direct-acting genotoxins

    Mutat Res

    (2004)
  • J. Zhou et al.

    Challenges in applying microarrays to environmental studies

    Curr Opin Biotechnol

    (2002)
  • E. Lammer et al.

    Is the fish embryo toxicity test (FET) with the zebrafish (Danio rerio) a potential alternative for the fish acute toxicity test?

    Comp Biochem Physiol C: Toxicol Pharmacol

    (2009)
  • K. van der Ven et al.

    Development and application of a brain-specific cDNA microarray for effect evaluation of neuro-active pharmaceuticals in zebrafish (Danio rerio)

    Comp Biochem Physiol B: Biochem Mol Biol

    (2005)
  • S.F. Altschul et al.

    Basic local alignment search tool

    J Mol Biol

    (1990)
  • V.J. McKelvey-Martin et al.

    The single cell gel electrophoresis (comet assay): a European review

    Mutat Res

    (1993)
  • A. Schnurstein et al.

    Tail moment versus tail length-application of an in vitro version of the comet assay in biomonitoring for genotoxicity in native surface waters using primary hepatocytes and gill cells from zebrafish (Danio rerio)

    Ecotoxicol Environ Saf

    (2001)
  • J.J. Schlezinger et al.

    Uncoupling of cytochrome P450 1A and stimulation of reactive oxygen species production by co-planar polychlorinated biphenyl congeners

    Aquat Toxicol

    (2006)
  • S. Hunter et al.

    Apolipoprotein D is down-regulated during malignant transformation of neurofibromas

    Hum Pathol

    (2005)
  • U. Langheinrich et al.

    Zebrafish as a model organism for the identification and characterization of drugs and genes affecting p53 signaling

    Curr Biol

    (2002)
  • T.X. Liu et al.

    Knockdown of zebrafish Fancd2 causes developmental abnormalities via p53-dependent apoptosis

    Dev Cell

    (2003)
  • S. Violante et al.

    Carnitine palmitoyltransferase 2: new insights on the substrate specificity and implications for acylcarnitine profiling

    Biochim Biophys Acta: Mol Basis Dis

    (2010)
  • Y. Liu et al.

    Induction of time-dependent oxidative stress and related transcriptional effects of perfluorododecanoic acid in zebrafish liver

    Aquat Toxicol

    (2008)
  • H. Zhang et al.

    Lipid homeostasis and oxidative stress in the liver of male rats exposed to perfluorododecanoic acid

    Toxicol Appl Pharmacol

    (2008)
  • P.A. Thompson et al.

    Comparison of DNA adduct levels associated with exogenous and endogenous exposures in human pancreas in relation to metabolic genotype

    Mutat Res

    (1999)
  • B. Brunström et al.

    EROD induction by environmental contaminants in avian embryo livers

    Comp Biochem Physiol

    (1998)
  • J. Wölz et al.

    Effect-directed analysis of Ah receptor-mediated activities caused by PAHs in suspended particulate matter sampled in flood events

    Sci Tot Environ

    (2010)
  • A.V. Hallare et al.

    Assessing contamination levels of Laguna Lake sediments (Philippines) using a contact assay with zebrafish (Danio rerio) embryos

    Sci Tot Environ

    (2005)
  • S. Airaksinen et al.

    Stressor-dependent regulation of the heat shock response in zebrafish, Danio rerio

    Comp Bioch Physiol A: Mol Int Physiol

    (2003)
  • S.R. Blechinger et al.

    Brief embryonic cadmium exposure induces a stress response and cell death in the developing olfactory system followed by long-term olfactory deficits in juvenile zebrafish

    Toxicol Appl Pharmacol

    (2007)
  • M. Wahl et al.

    A technical mixture of 2,2′,4,4′-tetrabromo diphenyl ether (BDE47) and brominated furans triggers aryl hydrocarbon receptor (AhR) mediated gene expression and toxicity

    Chemosphere

    (2008)
  • E.F. Nuwaysir et al.

    Microarrays and toxicology: the advent of toxicogenomics

    Mol Carcinogen

    (1999)
  • T. Lettieri

    Recent applications of DNA microarray technology to toxicology and ecotoxicology

    Environ Health Perspect

    (2006)
  • N.M. van Straalen

    Ecotoxicology becomes stress ecology

    Environ Sci Technol

    (2003)
  • R.R. Tice et al.

    Single cell gel/comet assay: guidelines for in vitro and in vivo genetic toxicology testing

    Environ Mol Mutagen

    (2000)
  • B.N. Ames et al.

    Methods for detecting carcinogens and mutagens with the Salmonella/mammalian-microsome mutagenicity test

    Mutat Res

    (1975)
  • J. Bartlett

    Technology evaluation: SAGE, genzyme molecular oncology

    Curr Opin Mol Ther

    (2001)
  • S. Gallègue-Zouitina et al.

    Adducts from in vivo action of the carcinogen 4-hydroxyaminoquinoline 1-oxide in rats and from in vitro reaction of 4-acetoxyaminoquinoline 1-oxide with DNA and polynucleotides

    Cancer Res

    (1985)
  • E.G. Sideris et al.

    Mutagenesis:carcinogenesis and the metal elements–DNA interaction

    Prog Clin Biol Res

    (1988)
  • T. Sanner et al.

    Studies of tumor promoters with the Syrian hamster embryo cell transformation assay

    Carcinog Compr Surv

    (1985)
  • C. Furihata et al.

    Induction of unscheduled DNA synthesis in rat stomach mucosa by glandular stomach carcinogens

    J Natl Cancer Inst

    (1984)
  • H.K. Hamadeh et al.

    Gene expression analysis reveals chemical-specific profiles

    Toxicol Sci

    (2002)
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