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Respiratory Strategies and Associated Exchange Epithelia As Determinants Redacted for Privacy Redacted for Privacy Abstrac AN ABSTRACT OF THE DISSERTATION OF David B. Buchwalter for the degree of Doctor of Philosophy in Toxicology presented on August 5, 2002. Title: Respiratory Strategies and Associated Exchange Epithelia as Determinants Redacted for Privacy Redacted for Privacy Abstrac Aquatic insects are used extensively to evaluate water quality. Despite their widespread use as indicator organisms, relatively little is known about the organismal characteristics that determine sensitivity differences to individual and multiple stressors. Insects have evolved several respiratory strategies that range from breathing atmospheric air to utilizing dissolved oxygen in water via exchange epithelial surfaces. This dissertation examines the role of respiratory attributes in determining differential accumulation of the insecticide chlorpyrifos, and further examines how accumulation rates are affected by temperature shifts. In addition, the relative roles of uptake rates and target site sensitivity differences are examined among developmental stages of the aquatic midge, C. riparius. Major findings: Smaller, gill-bearing insects accumulate chiorpyrifos and water at higher rates than larger, air-breathing insects. .Chiorpyrifos and water accumulation rates are highly covariant in aquatic insects. Temperature increases affect chiorpyrifos accumulation rates in dissolved oxygen breathers more so than in air-breathers. .Earlier instars of C. riparius are more sensitive to chiorpyrifos than later instars. Sensitivity differences among2nd4thinstar C. riparius are largely due to differences in chiorpyrifos accumulation rates. Respiratory Strategies and Associated Exchange Epithelia as Determinants of Contaminant Uptake in Aquatic Insects. by David B. Buchwalter A DISSERTATION Submitted to Oregon State University In partial fulfillment of the requirements for the degree of Doctor of Philosophy Presented August 5, 2002 Commencement June, 2003 Doctor of Philosophy dissertation of David B. Buchwalter presented on August 5, 2002. APPROVED: Redacted for Privacy Co-f*tjor professor, representing fox[c6iogy Redacted for Privacy Co Toxicology Redacted for Privacy Heid of the Department of Envit'onTmehtl & Molecular Toxicology Redacted for Privacy Dean of the fi1aduate School I understand that my dissertation will become part of the pennanent collection of Oregon State University libraries. My signature below authorizes release of my dissertation to any reader upon request. Redacted for Privacy David B. Buchwalter, Author ACKNOWLEDGEMENTS The author expresses sincere appreciation for the contributions of several individuals. My co-advisors, Dr. Larry Curtis and Dr. Jeff Jenkins provided me with their technical expertise, guidance, and support throughout this project. Dr. Darlene Judd in the Entomology Department at Oregon State University was also tremendously helpful. Jason Sandahl provided his efforts and expertise in cholinesterase assays that were a substantial contribution to Chapter 4 of this document. Wanda Parrott provided endless editorial assistance and good cheer throughout my time at OSU. CONTRIBUTION OF AUTHORS Each of these manuscripts has been co-authored by Dr. Lawrence R. Curtis and Dr. Jeffrey J. Jenkins. In addition, Chapter four was co-authored by Jason Sandahi. TABLE OF CONTENTS Page Introduction .1 2. Respiratory Strategy is a Major Determinant of Temperature-Modulated 3H20 Flux and14C-Chlorpyrifos Uptake in Aquatic Insects..................9 3. Respiratory Strategy is a Major Determinant of [3H]-Water and ['4C]- Chiorpyrifos Uptake in Aquatic Insects........................................31 4. Roles of Uptake and Target Site Sensitivity in Determining the Differential Toxicity of Chlorpyrifos to2nd 4thInstar Chironomous riparius .............................................................................. 52 5. Future Directions ................................................................... 68 Bibliography.................................................................................78 LIST OF FIGURES Figure Page Electron micrographs of a single Pteronarcys californica gill tuft.......10 2. The influence of temperature on 3H2O accumulation in the hemoiymph of Pteronarcys calfornica.......................................19 Effects of temperature shifts and acclimation on water influx.............21 4. 14C-Inuiin carboxyl was used to determine hemolymph volumes in P. californica..................................................................22 5. The influence of respiratory strategy, temperature and size on 3H2O accumulation in three species of aquatic insects............................24 6. Temperature influences the rates of chlorpyrifos uptake in the air-breathing hemipteran Sigara washingtonensis and the gill-bearing ephemeropteran Cinygma (sp).................................................25 7. Water permeability in aquatic insects is expressed in terms of percent body water based on the accumulation of H20 relative to total body water composition ................................................................ 39 Water permeability in aquatic insects is a function of both body size and respiratory strategy..........................................................40 9. Chiorpyrifos uptake rates in aquatic insects are determined by body size and respiratory strategy..................................................... 42 10. Chiorpyrifos uptake rates vs. water permeability in aquatic insect taxa...43 11. Diphenyihaxatriene (DPH) labeled C. riparius (below) and Psectrotanypus sp. (above)....................................................... 45 12. Time to death for C.riparius larvae exposed to 0.53 5 mg/i '4C- chiorpyrifos and associated body burdens...................................... 60 214th 13. Chiorpyrifos accumulation in instar C. riparius larvae................61 LIST OF FIGURES (CONTINUED) Figure 14. In vitro acetyicholinesterase activity associated with exposure to chiorpyrifos-oxon and chiorpyrifos in C. riparius homogenates derived from2nd4thinstar larvae ................................................. 63 15. Surface area vs body weight in ethanol-fixed versusCO2anesthetized C. riparius larvae ................................................................... 64 Respiratory Strategies and Associated Exchange Epithelia as Determinants of Contaminant Uptake in Aquatic Insects INTRODUCTION Aquatic insects play important ecological roles in freshwater ecosystems and are used extensively to evaluate water quality. Freshwater ecosystems may be subjected to a variety of natural and anthropogenic stressors. That the biotic components of disturbed systems may be differentially affected by a stressor is the basis for the use of ecological indicators and bioassessment efforts. Ecological communities retain information about events in their history (Mafthews et al, 1996). The attempt to use biological indices in the assessment of water quality has been continually developing for the past 150 years (Hynes 1960; Woodiwiss 1964;; Plafkinetal.1989; Davis 1995). Bioassessment efforts using macroinvertebrates have resulted in cost-effective and increasingly useful techniques for regulatory agencies across the Unites States and Europe (Plafkinetal.1989). In the United States, bioassessment is an important feature of sections 303(c), 303(d), 305(b), and 402 of the Clean Water Act. Traditionally, water quality monitoring has involved taking water samples, measuring various physical and chemical characteristics, and comparing these measurements to standards. This approach, while providing important information, has proven to be expensive, and does not take into consideration "beneficial uses" such as the health of the resident biota. Despite its widespread use, there is substantial room for improvement in bioassessment. The current bioassessment techniques using aquatic macroinvertebrates are not stressor-specific. The same techniques or metrics are used for all types of situations, and tend to treat all stressor types equally (i.e. temperature, sedimentation, pH, soluble contaminants, sediment bound contaminants, flow regimes, physical habitat alterations). While current bioassessment approaches may be appropriate for making generalizations about ecosystem integrity, they lack the mechanistic specificity required to determine causal relationships, which are ultimately important for management. The existing methodologies for bioassessment are based on ecological survey data. Observations made by numerous ecologists in tremendously varied aquatic ecosystems have essentially been codified into the practices that are in place today. The end result of this process is that current techniques are not built upon experimental data and/or studies designed to test hypotheses. For example, the Environmental Protection Agency (EPA) advocates the use of tolerance values for individual species. These tolerance values are not stressor specific. A single value is given to a taxon, which is intended to reflect its tolerance to a wide variety of stressors, such as sedimentation, chemical contaminants, altered flow regimes, and dissolved oxygen, to name several. This simplistic approach is, in part, due to our limited understanding of the organismal characteristics that mediate aquatic insect responses to individual stressors. As bioassessment advances increasingly into the regulatory arena in several states, there is clearly a need to further develop and refine bioassessment techniques such that they are more scientifically defensible. There are over
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