Zoarces Viviparus) Females and Larvae
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Environmental Toxicology and Chemistry, Vol. 34, No. 7, pp. 1511–1523, 2015 Published 2015 SETAC Printed in the USA Environmental Toxicology A GENE TO ORGANISM APPROACH—ASSESSING THE IMPACT OF ENVIRONMENTAL POLLUTION IN EELPOUT (ZOARCES VIVIPARUS) FEMALES AND LARVAE NOOMI ASKER,*y BETHANIE CARNEY ALMROTH,y EVA ALBERTSSON,y MARIATERESA COLTELLARO,z JOHN PAUL BIGNELL,x NIKLAS HANSON,y VITTORIA SCARCELLI,z BJoRN€ FAGERHOLM,k JARI PARKKONEN,y EMMA WIJKMARK,# GIADA FRENZILLI,z LARS Fo€RLIN,y and JOACHIM STURVEy yDepartment of Biological and Environmental Sciences, University of Gothenburg, Gothenburg, Sweden zDepartment of Clinic and Experimental Medicine, University of Pisa, Pisa, Italy xCentre for Environment, Fisheries and Aquaculture Science, Weymouth, Dorset, United Kingdom kDepartment of Aquatic Resources, Institute of Coastal Research, Swedish University of Agricultural Sciences, V€arobacka,€ Sweden #Department of Mathematical Statistics, Chalmers University of Technology, Gothenburg, Sweden (Submitted 17 September 2014; Returned for Revision 26 October 2014; Accepted 1 February 2015) Abstract: A broad biomarker approach was applied to study the effects of marine pollution along the Swedish west coast using the teleost eelpout (Zoarces viviparus) as the sentinel species. Measurements were performed on different biological levels, from the molecular to the organismal, including measurements of messenger RNA (mRNA), proteins, cellular and tissue changes, and reproductive success. Results revealed that eelpout captured in Stenungsund had significantly higher hepatic ethoxyresorufin O-deethylase activity, high levels of both cytochrome P4501A and diablo homolog mRNA, and high prevalence of dead larvae and nuclear damage in erythrocytes. Eelpout collected in Goteborg€ harbor displayed extensive macrovesicular steatosis, whereby the majority of hepatocytes were affected throughout the liver, which could indicate an effect on lipid metabolism. Results also indicate that eelpouts collected at polluted sites might have an affected immune system, with lower mRNA expression of genes involved in the innate immune system and a higher number of lymphocytes. Biomarker assessment also was performed on livers dissected from unborn eelpout larvae collected from the ovary of the females. No significant differences were noted, which might indicate that the larvae to some extent are protected from effects of environmental pollutants. In conclusion, usage of the selected set of biological markers, covering responses from gene to organism, has demonstrated site-specific biomarker patterns that provided a broad and comprehensive picture of the impact of environmental stressors. Environ Toxicol Chem 2015;34:1511–1523. # 2015 The Authors. This is an open access article under the terms of the Creative Commons Attribution-NonCommercial License, which permits use, distribution and reproduction in any medium, provided the original work is properly cited and is not used for commercial purposes. Keywords: Biomarker Histopathology Genotoxicity Gene expression Eelpout INTRODUCTION these results, appropriate measures can be taken to avoid adverse fi Many coastal environments are contaminated with a variety effects at higher biological levels. Biomarker responses in sh of chemicals that are produced through industrial effluents, and other aquatic organisms have been employed in many agricultural runoff, and domestic waste. Pollutants are found in environmental monitoring programs to assess the impact of different mixtures, and their concentration could vary over time pollutants. Studies using multibiomarker approaches provide the because some are persistent and others only occasionally opportunity to correlate different effects, to guide biomarker released into the environment. Different life stages, such as selections, and to obtain a more holistic picture of the impact of – larvae development, can be more sensitive to exposure. There is contaminants [1 4]. fi a lack of understanding of the effects of chronic pollution on The eelpout (Zoarces viviparus) is a marine sh species that individual fish and fish populations as well as a large knowledge is widespread in the coastal waters of northern Europe, and it gap concerning the effects of complex mixtures of chemicals, used as sentinel species in the present study. It lives in relatively such as those seen in most coastal environments. Assessment of stationary populations, and because of this, contaminant loads the effects of chronic pollution is therefore important to be able and biological responses detected in the eelpout most likely fl to protect the organisms in the aquatic environment from re ect the environmental condition, including pollutants, within disruption of reproductive status and to avoid possible decline in the area where it is captured. The eelpout has been used in fish stocks and biodiversity. environmental monitoring studies for several decades in To study and understand the effects of environmental Sweden, Denmark, and Germany [5]. The eelpout has been pollutants, biological markers such as biomarkers often are recommended as a suitable species for studying and monitoring used. Biomarkers indicate a change in biological response to pollutant effects in marine coastal waters by the International exposure or effects of xenobiotics. These biomarker responses Council for the Exploration of the Sea, the Baltic Marine often are early warning signs that can pinpoint polluted sites and Environment Protection Commission, the Convention for the identify previously unknown sources of pollutants. Based on Protection of the Marine Environment of the North-East Atlantic, and the Swedish Environmental Protection Agency. Eelpout mate at the end of August, and the larvae hatch All Supplemental Data may be found in the online version of this article. approximately 3 wk later, inside the female, where they develop * Address correspondence to [email protected] fi Published online 7 February 2015 in Wiley Online Library for 4 mo to 5 mo [6]. Thus, in contrast to most sh species that (wileyonlinelibrary.com). lay eggs, the viviparous eelpout provides a unique opportunity DOI: 10.1002/etc.2921 to link responses in the individual female fish to ecologically 1511 1512 Environ Toxicol Chem 34, 2015 N. Asker et al. relevant parameters, such as reproduction and larvae develop- Reagents were products of Bio-Rad Laboratories; and the ment. Guidelines for sampling and assessment criteria for the RNeasy Plus Mini Kit was purchased from Qiagen. All other frequency of abnormal larvae in broods have been suggested by chemicals were of analytical grade. the International Council for the Exploration of the Sea [7]. Three polluted sites along the Swedish west coast (the Sampling sites Goteborg€ harbor, Stenungsund, and Brofjorden) were used in the Five different locations on the Swedish west coast were present study. The Goteborg€ harbor is the largest general oil port selected (Figure 1): Goteborg€ harbor (57.68668N, 11.7528E), in Scandinavia. The harbor has been involved in environmental Stenungsund (58.09738N, 11.82518E), Brofjorden (58.35368N, monitoring conducted by our group for several years, in addition 11.41848E), Billdal (57.58278N, 11.91418E), and Fj€allbacka to studies conducted during dredging activities and after a big oil (58.64408N, 11.24578E). Fj€allbacka was used as reference site spill in 2003 [8–10]. Stenungsund is located in the vicinity of the for all measurements in the present study except for the largest petrochemical industry in Sweden. Brofjorden is situated genotoxicity study, for which Billdal also was included as a close to an oil refinery and is Sweden’s 2nd largest oil harbor. reference site. Goteborg€ harbor, located in the outlet of the Gota€ Earlier studies on eelpout collected at Stenungsund and €alv River, is the largest general oil port in Scandinavia. The Brofjorden revealed a higher prevalence of dead and malformed harbor water and sediment are known to be contaminated with eelpout larvae in these sites compared with other sites along the various anthropogenic substances and several toxic compounds, Swedish west coast [11,12]. Two reference sites also were including PCBs, PAHs, tributyltin, dioxins, and heavy metals included in the present study: Fj€allbacka, a national reference such as Hg [16–18]. Stenungsund is located in the vicinity of the site used by the Swedish Environmental Protection Agency, and largest petrochemical industry in Sweden. Many chemical Billdal, located south of Goteborg.€ Both of these are considered industries are concentrated in the area including, a large naphtha to be sites with low anthropogenic impact. Eelpouts collected cracker, and the area is known to be polluted with PAHs, from Fj€allbacka have been involved in annual biomonitoring hexachlorobenzene, octylphenol, and tributyltin [11,19]. Brof- since 1989 [13]. Many of the environmental contaminants found jorden is located close to an oil refinery and is Sweden’s 2nd in Goteborg€ harbor, Stenungsund, and Brofjorden are commonly largest oil harbor. This site is also known to be contaminated found in coastal areas and include chemicals such as polycyclic with PAHs, tributyltin, PCBs, and polybrominated diphenyl hydrocarbons (PAHs), metals (e.g., Cd, Cr, and Hg), organo- ethers [19]. chlorinated contaminants (e.g., polychlorinated biphenyls [PCBs]), and organotins (e.g., tributyltin). These contaminants Sampling of fish and dissection are known to have toxic effects in fish, including immunotoxic, Eelpout