Ecological implications of molecular biomarkers: assaying sub-lethal stress in the midge Chironomus tentans using heat shock protein 70 HSP-70) expression

  • N. K. Karouna-Renier
  • J. P. Zehr
Part of the Developments in Hydrobiology book series (DIHY, volume 138)

Abstract

Aquatic community structure is a reflection of the changes in constituent populations and the complex interactions between these organisms and environmental Stressors. Consequently, shifts in populations and community structure can be used to assess water quality. However, these indicators only reflect damage already sustained by an ecosystem and are not useful for prediction of potential ecological impacts. Molecular/biochemical indicators, such as heat shock proteins, can provide early indication of environmental stress on aquatic communities. The heat shock protein response involves the synthesis of an array of proteins that protect organisms from cellular damage resulting from exposure to a variety of Stressors. Consequently, stress proteins have the potential of being an important screening tool indicating exposure to, and/or biological effects of environmental contaminants. The midge larva Chironomus tentans has been extensively used in bioassays of freshwater systems. However, investigations of stress proteins as environmental biomarkers in midges are lacking. To evaluate the potential use of HSP-70 as a biomarker of environmental stress, we completed a preliminary characterization of the stress protein response in C. tentans upon exposure to heat shock. Western immunoblotting indicated an increase in a 72 kD protein after larvae were exposed to 33 °C, 35 °C, and 37 °C. The observed induction was rapid, appearing within 5-10 min, and persisted for over 24 h after removal of the Stressor. The results are discussed with regard to the use of the HSP-70 biomarker as an environmental screening tool. It is proposed that the HSP-70 biomarker is most applicable as a sublethal toxicity test endpoint indicative of the presence of biochemically significant levels of stress.

Key words

HSP-70 Chironomus tentans heat shock biomarkers 

Preview

Unable to display preview. Download preview PDF.

Unable to display preview. Download preview PDF.

References

  1. APHA, 1992. Standard Methods for the Examination of Water and Wastewater. American Public Health Association, Washington, D.C.Google Scholar
  2. Attrill, M. J. & M. H. Depledge, 1997. Community and population indicators of ecosystem health: targeting links between levels of biological organization. Aquat. Toxicol. 38: 183–197.CrossRefGoogle Scholar
  3. Barettino, D., G. Morcillo & J. L. Diez, 1988. Induction of the heat shock response by carbon dioxide in Chironomus thummi. Cell Differentiation 23: 27–36.PubMedCrossRefGoogle Scholar
  4. Benoit, D. A., P. K. Sibley, J. L. Juenemann & G. T. Ankley, 1997. Chironomus tentans life-cycle test: design and evaluation for use in assessing toxicity of contaminated sediments. Environ. Toxicol. Chem. 16: 1165–1176.Google Scholar
  5. Burton, G. A. & C. MacPherson, 1995. Sediment toxicity testing issues and methods. In Hoffmann D. A., B. A. Rattner, G.A. Burton & J. Cairns (eds), Environmental Toxicology. Lewis Publishers, CRC Press, Inc., Boca Raton (FL): 70–103.Google Scholar
  6. Carretero, M. T., M. J. Carmona, & J. L. Diez, 1991. Thermotol-erance and heat shock proteins in Chironomus. J. Insect Physiol. 37: 239–246.CrossRefGoogle Scholar
  7. Clements, W. H., D. S. Cherry & J. Cairns, Jr., 1988. Impact of heavy metals on insect communities in streams: a comparison of observational and experimental results. Can. J. Fish. aquat. Sci. 45: 2017–2025.CrossRefGoogle Scholar
  8. Dyer, S. D. 1991. Evaluation of the efficacy of the stress protein response as a biochemical water quality monitoring method. University of North Texas, Denton, TX.Google Scholar
  9. Dyer, S. D., G. L. Brooks, K. L. Dickson, B. M. Sanders & E. G. Zimmerman, 1993. Synthesis and accumulation of stress proteins in tissues of arsenite-exposed fathead minnows (Pimephales promelas). J. Toxicol. Chem. 12: 913–9Google Scholar
  10. Fader, S. C., Z. Yu & J. R. Spotila. 1994. Seasonal variation in heat shock proteins (HSP70) in stream fish under natural conditions. J. Therm. Biol. 19:335–341.CrossRefGoogle Scholar
  11. Johnson, R. K., T. Wiederholm & D. M. Rosenberg, 1993. Freshwater biomonitoring using individual organisms, populations, and species assemblages of benthic macroinvertebrates. In Rosenberg D. M. & V. H. Resh (eds), Freshwater Biomonitoring and Benthic Macroinvertebrates. Chapman & Hall, Inc., New York, NY: 40–125.Google Scholar
  12. Köhler, H.-R., B. Rahman, S. Graff, M. Berkus & R. Triebskorn, 1996. Expression of the stress-70 protein family due to heavy metal contamination in the slug, Derocerus reticulatum: an approach to monitor sublethal stress conditions. Chemosphere 33: 1327–1340.CrossRefGoogle Scholar
  13. Laemmli, U. K., 1970. Cleavage of structural proteins during the assembly of the head of bacteriophage T4. Nature 227: 680–685.PubMedCrossRefGoogle Scholar
  14. Lezzi, M., B. Meyer & R. Mahr, 1981. Heat shock phenomena in Chironomus tentons I. In vivo effects of heat, overheat and quenching on salivary chromosome puffing. Chromosoma (Berl.) 83: 327–339.PubMedCrossRefGoogle Scholar
  15. Morcillo, G., & J. L. Diez, 1996. Telomeric puffing induced by heat shock in Chironomus thummi. J. Biosci. 21: 247–257.CrossRefGoogle Scholar
  16. Ritossa, F. M., 1962. A new puffing pattern induced by heat shock and DNP in Drosophila. Experimentia 18: 571–573.CrossRefGoogle Scholar
  17. Ryan, J. A. & L. E. Hightower, 1994. Evaluation of heavy-metal ion toxicity in fish cells using a combined stress protein and cytotoxicity assay. Environ. Toxicol. Chem. 13: 1231–1240.CrossRefGoogle Scholar
  18. Sanders, B., 1990. Stress proteins: potential as multitiered bio-markers. In Shugart L., J. McCarthy (eds), Biomarkers of Environmental Contamination. Lewis Publishers, Boca Raton (FL): 165–191.Google Scholar
  19. Sanders, B. M., 1993. Stress proteins in aquatic organisms: an environmental perspective. CRC Crit. Rev. Toxicol. 23: 49–75.CrossRefGoogle Scholar
  20. Sanders, B. M., L. S. Martin, P. A. Nakagawa, D. A. Hunter & S. Miller, 1994. Specific cross-reactivity of antibodies raised against two major stress proteins, stress 70 and chaperonin 60, in diverse species. Environ. Toxicol. Chem. 13: 1241–1249.CrossRefGoogle Scholar
  21. Sanders, B. M., L. S. Martin, W. G. Nelson, D. K. Phelps & W. Welch, 1991. Relationships between accumulation of a 60-kDa stress protein and scope-for-growth in Mytilus edulis exposed to a range of copper concentrations. Mar. envir. Res. 31: 81–97.CrossRefGoogle Scholar
  22. Sanders, B. M., J. Nguyen, L. S. Martin, S. R. Howe & S. Coventry, 1995. Induction and subcellular localization of two major stress proteins in response to copper in the fathead minnow Pimephales promelas. Comp. Biochem. Physiol. 112C: 335–343.Google Scholar
  23. Sibley, P. K., D. A. Benoit & G. T. Ankley, 1997. The significance of growth in Chironomus tentans sediment toxicity tests: relationship to reproduction and demographic endpoints. Environ. Toxicol. Chem. 16: 336–345.Google Scholar
  24. Simpson, K. W., R. W. Bode & J. R. Colquhoun, 1985. The macroin-vertebrate fauna of an acid-stressed headwater stream system in the Adirondack Mountains, New York. Freshwat. Biol. 15: 671–681.CrossRefGoogle Scholar
  25. Smerdon, G. R., J. P. Chappie & A. J. S. Hawkins, 1995. The simultaneous immunological detection of four Stress-70 protein isoforms in Mytilus edulis. Mar. envir. Res. 40: 399–407.CrossRefGoogle Scholar
  26. Stegeman, J. J., M. Brouwer, R. T. Di Giullo, L. Forlin, B. A. Fowler, B. M. Sanders & P. A. Van Veld, 1992. Molecular responses to environmental contamination: enzyme and protein systems as indicators of chemical exposure and effect. In Hug-gett R. J., R. A. Kimerle, P. M. Mehrle Jr. & H. L. Bergman (eds), Biomarkers: Biochemical, Physiological, and Histological Markers of Anthropogenic Stress. Lewis Publishers, Inc., Ann Arbor (MI): 235–335.Google Scholar
  27. Tanguay, R. M. & M. Vincent, 1980. Biosynthesis and characterization of heat shock proteins in Chironomus tentans salivary glands. Can. J. Biochem. 59: 67–73.Google Scholar
  28. U.S. EPA (United States Environmental Protection Agency), 1994. Methods for measuring the toxicity and bioaccumulation of sediment associated contaminants using freshwater invertebrates. EPA 600-R94-024. Technical Report. Washington, DC.Google Scholar
  29. Veldhuizen-Tsoerkan, M. B., D. A. Holwerda, C. A. van der Mast & D. I. Zandee, 1990. Effects of cadmium exposure and heat shock on protein synthesis in gill tissue of the sea mussel Mytilus edulis L. Comp. Biochem. Physiol. C. 96: 419–426.Google Scholar
  30. Veldhuizen-Tsoerkan, M. B., D. A. Holwerda, C. A. van der Mast & D. I. Zandee, 1991. Synthesis of stress proteins under normal and heat shock conditions in gill tissue of sea mussels (Mytilus edulis) after chronic exposure to cadmium. Comp. Biochem. Physiol. 100: 699–7Google Scholar
  31. Yu, Z., W. E. Magee & J. R. Spotila, 1994. Monoclonal antibody ELISA test indicates that large amounts of constitutive HSP-70 are present in salamanders, turtle and fish. J. therm. Biol. 19: 41–53.CrossRefGoogle Scholar

Copyright information

© Springer Science+Business Media Dordrecht 1999

Authors and Affiliations

  • N. K. Karouna-Renier
    • 1
  • J. P. Zehr
    • 1
  1. 1.Department of BiologyRensselaer Polytechnic InstituteTroyUSA

Personalised recommendations