BMC Research Notes | |
Effects of mining chemicals on fish: exposure to tailings containing Lilaflot D817M induces CYP1A transcription in Atlantic salmon smolt | |
Torstein Kristensen2  John B. Ulvund3  Tom O. Nilsen4  Henning A. Urke5  Pål A. Olsvik1  | |
[1] National Institute of Nutrition and Seafood Research, Nordnesboder 1-2, Bergen, 5005, Norway;Faculty of Biosciences and Aquaculture, University of Nordland, Bodø, 8049, Norway;Norwegian Institute of Water Research, Trondheim, 7486, Norway;UNI Research, Bergen, 5006, Norway;INAQ AS, Trondheim, 7462, Norway | |
关键词: Transcriptional responses; Lilaflot D817M; Flotation chemicals; Atlantic salmon; Mining activity; | |
Others : 1230437 DOI : 10.1186/s13104-015-1342-2 |
|
received in 2014-08-08, accepted in 2015-08-12, 发布年份 2015 | |
【 摘 要 】
Background
Mine tailings, containing metals and production chemicals such as flotation chemicals and flocculants, may pose an environmental threat to aquatic organisms living in downstream ecosystems. The aim of this work was to study to which degree Lilaflot D817M, a flotation chemical extensively used by the mining industry, represents a hazard for migrating salmon in rivers affected by mining activity. Smoltifying Atlantic salmon were exposed to four concentrations of iron-ore mine tailings containing residual Lilaflot D817M [water versus tailing volumes of 0.002 (Low), 0.004 (Medium), 0.013 (High) and 0.04 (Max)]. After 96 h of exposure, gill and liver tissues were harvested for transcriptional responses. Target genes included markers for oxidative stress, detoxification, apoptosis and DNA repair, cell signaling and growth.
Results
Of the 16 evaluated markers, significant transcriptional responses of exposure to tailings enriched with Lilaflot D817M were observed for CYP1A, HSP70 and HMOX1 in liver tissue and CYP1A in gill tissue. The significant induction of CYP1A in both liver and gills suggest that the flotation chemical is taken up by the fish and activates cytochrome P450 detoxification via phase I biotransformation in the cells.
Conclusions
The overall weak transcriptional responses to short-term exposure to Lilaflot D817M-containing iron-ore tailings suggest that the mining chemical has relatively low toxic effect on fish. The underlying mechanisms behind the observed CYP1A induction should be studied further.
【 授权许可】
2015 Olsvik et al.
【 预 览 】
Files | Size | Format | View |
---|---|---|---|
20151106073240929.pdf | 1513KB | download | |
Fig.4. | 31KB | Image | download |
Fig.3. | 34KB | Image | download |
Fig.2. | 67KB | Image | download |
Fig.1. | 68KB | Image | download |
【 图 表 】
Fig.1.
Fig.2.
Fig.3.
Fig.4.
【 参考文献 】
- [1]Luoma SN, Rainbow PS: Metal contamination in aquatic environments. Cambridge University Press, New York; 2011.
- [2]Liber K, Weber L, Levesque C: Sublethal toxicity of two wastewater treatment polymers to lake trout fry (Salvelinus namaycush). Chemosphere 2005, 61:1123-1133.
- [3]Skei JM, Syvitski JPM. Natural flocculation of mineral particles in seawater—influence on mine tailings sea disposal and particle dispersal. Mineralproduksjon. 2013;3:A1–A10.. http://mineralproduksjon.no/wp-content/uploads/2014/03/mp3-00-hele.pdf webcite
- [4]Klif. Bergverk og avgangsdeponering, Status, miljøutfordringer og kunnskapsbehov. Klima og Forurensnings Direktoratet (Klif) TA 2715;2010 (In Norwegian, English summary).
- [5]Thorstad EB, Uglem I, Arechavala-Lopez P, Økland F, Finstad B: Low survival of hatchery-released Atlantic salmon smolts during initial river and fjord migration. Boreal Environ Res 2011, 16:115-120.
- [6]EPA. Fatty nitrogen derived amines category high production volume (HPV) chemicals challenge. Assessment of data availability and test plan. Prepared for American Chemistry Council’s Fatty Nitrogen Derivatives Panel Amines Task Group. Prepared by Toxicology/Regulatory Services, Inc. 201-14171a. 2003.. http://www.epa.gov/hpv/pubs/summaries/amines/c14171rt1.pdf webcite
- [7]Berge JA. Gruvekjemikalier i sedimentene i sjøområdene utenfor Kirkenes i 2009. Niva rapport L.NR. 5860-2009. 2009 (In Norwegian, English summary).
- [8]Berge JA. Giftighetstester med flotasjonskjemikaliet Lilaflot D817M. Effekter på alger, børstemark, krepsdyr of fisk. NIVA rapport L.NR. 6044-2010 (In Norwegian, English summary).
- [9]Schlenk D, Celander M, Gallagher EP, George S, James M, Kullman SW, Hurk PVD, Willett K: Biotransformation in fishes. In The toxicology of fishes. Edited by Giulio RT, Hinton DE. CRC Press, Boca Raton; 2008:153-234.
- [10]Tully DB, Collins BJ, Overstreet JD, Smith CS, Dinse GE, Mumtaz MM, Chapin R: Effects of arsenic, cadmium, chromium, and lead on gene expression regulated by a battery of 13 different promoters in recombinant HepG2 cells. Toxicol Appl Pharmacol 2000, 168:79-90.
- [11]Korashy HM, Ei-Kadi AOS: The role of redox-sensitive transcription factors NF-kappa B and AP-1 in the modulation of the Cyp1a1 gene by mercury, lead, and copper. Free Rad Biol Med 2008, 44:795-806.
- [12]Søfteland L, Holen E, Olsvik PA: Toxicological application of primary hepatocyte cell cultures of Atlantic cod (Gadus morhua)—effects of BNF, PCDD and Cd. Comp Biochem Physiol C-Toxicol Pharmacol 2010, 151:401-411.
- [13]Rana Gruber.. http://www.ranagruber.no/index.php?id=50&L=1 webcite
- [14]Kroglund F, Finstad B, Stefansson SO, Nilsen TO, Kristensen T, Rosseland BO, Teien HC, Salbu B: Exposure to moderate acid water and aluminum reduces Atlantic salmon post-smolt survival. Aquacult 2007, 273(2–3):360-373.
- [15]Nilsen TO, Ebbesson LOE, Kverneland OG, Kroglund F, Finstad B, Stefansson SO: Effects of acidic water and aluminum exposure on gill Na+, K+-ATPase alpha-subunit isoforms, enzyme activity, physiology and return rates in Atlantic salmon (Salmo salar L.). Aquat Toxicol 2010, 97(3):250-259.
- [16]GeneCards Database.. http://www.genecards.org webcite
- [17]Plantalech Manel-La N, Thorstad EB, Davidsen JG, Økland F, Sivertsgård R, McKinley RS, Finstad B: Vertical movements of Atlantic salmon post-smolts relative to measures of salinity and water temperature during the first phase of the marine migration. Fish Manag Ecol 2009, 16:147-154.
- [18]Bustin SA, Benes V, Garson JA, Hellemans J, Huggett J, Kubista M, Mueller R, Nolan T, Pfaffl MW, Shipley GL, Vandesompele J, Wittwer CT: The MIQE guidelines: minimum information for publication of quantitative real-time PCR experiments. Clin Chem 2009, 55:611-622.
- [19]Olsvik PA, Lindgren M, Maage A: Mercury contamination in deep-water fish: transcriptional responses in tusk (Brosme brosme) from a fjord gradient. Aquat Toxicol 2013, 144:172-185.
- [20]Vandesompele J, De Preter K, Pattyn F, Poppe B, Van Roy N, De Paepe A, Speleman F: Accurate normalization of real-time quantitative RT-PCR data by geometric averaging of multiple internal control genes. Genome Biol 2002, 3:RESEARCH0034. BioMed Central Full Text