ABSTRACT ELECTROPHYSIOLOGICAL RESPONSES OF THE LATERAL LINE AND HEART TO STRESSES OF HYPOXIA, CYANIDE, AND DDT IN RAINBOW TROUT BY Thomas Gordon Bahr Studies of lateral-line nerve and heart reSponses in rainbow trout, Salmo gairdnerii, to certain pollutional stresses are presented. Spontaneous and evoked lateral-line neural discharges and electrocardiograms were measured ig_§i£3 from curarized preparations exposed to hypoxic and aSphyxic conditions, and cyanide and DDT poisoning. ASphyxiation and cyanide poisoning caused a reduction in heart rate, changed wave forms of the electrocardiogram, and depressed both Spontaneous and evoked activity from the lateral—line nerve. Evoked reSponses persisted longer under stress than spontaneous activity. Discontinuation of stress was followed by recovery of both heart and lateral- line activity. Normal function of the lateral line is de- pendent on blood circulation and it is believed that ischemic conditions in the lateral line were responsible for the depressing effects of the stresses. :trézt‘ns‘ngwmgit‘w :1!“ WW 7' r71 2:11-51 Thomas Gordon Bahr Intravenous injection and water exposure to DDT caused little if any change in lateral line or heart activity. No change of these parameters was observed in fish suffer- ing characteristic DDT poisoning tremors. Hypoxic conditions resulted in a slight decrease of the heart rate and changes in the electrocardiogram were noted. Electrical activity recorded from the lateral—line nerve remained unchanged. The methodology developed for this study proved to be a useful tool for analyzing neurotoxic effects of pollution- related stresses. ELECTROPHYSIOLOGICAL RESPONSES OF THE LATERAL LINE AND HEART TO STRESSES OF HYPOXIA, CYANIDE, AND DDT IN RAINBOW TROUT BY Thomas Gordon Bahr A THESIS Submitted to Michigan State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY Department of Fisheries and Wildlife 1968 454/02/ 5-/d’—6‘7 ACKNOWLEDGMENTS I wish to express my sincere gratitude to Dr. Robert C. Ball for his helpful guidance and stimulation throughout my graduate program. His unselfish willingness in allowing me the freedom to pursue the topic of this thesis was also most greatful. I am indebted to Dr. Ralph A. Pax for his invaluable assistance in many phases of this study. His generosity in loaning me equipment is kindly appreciated. My appreciation is also extended to Dr. Paul O. Fromm and Dr. Niles R. Kevern for their helpful comments and con— tinual efforts on my behalf. I thank Dr. Harry K. Stevens for the many hours he Spent critically reading the manuscript. This study was financially supported by a Predoctoral Research Fellowship (5-Fl-WP-26,004-05) Sponsored by the Federal Water Pollution Control Administration of the United States Department of the Interior. ii TABLE OF CONTENTS Page INTRODUCTION . . . . . . . . . . . . . . . . . . . . . 1 LITERATURE REVIEW. . . . . . . . . . . . . . . . . . . 6 METHODS. . . . . . . . . . . . . . . . . . . . . . . . 12 Fish Holding and Feeding. . . . . . . . . . . . . 12 Experimental Fish Chamber . . . . . . . . . . . . 15 Surgical Methods. . . . . . . . . . . . . . . . . 19 Immobilization . . . . . . . . . . . . 19 Exposure of the lateral— line nerve . . . . . 21 Canulation of the cardinal vein. . . . . . . 26 Electrophysiological Methods. . . . . . . . . . 28 Recording from the lateral— line nerve. . . . 28 Recording electrical activity from the heart 29 Instrumentation. . . . . . . . . . . . . . . 50 Stimulation of lateral—line receptors. . . . 54 Chemical Methods. . . . . . . . . . . . . . . . . 42 DDT. . . . . . . . . . . . . . . . . . . . . 42 Cyanide. . . . . . . . . . . . . . . . . . . 44 Tubocurarine . . . . . . . . . . . . . . . . 44 Saline . . . . . . . . . . . . . . . . . . . 44 RESULTS. . . . . . . . . . . . . . . . . . . . . . . . 46 Experiments on Control Fish . 46 Spontaneous activity from the lateral line . 46 General observations. . . . . . . . . . 46 Nerve cutting experiments . . . . . . 48 Evoked activity from the lateral line. . . . 54 Electrical activity from the heart . . . . . 60 Experiments on Stressed Fish. . . . . . . . . . . 64 DDT experiments. . . . . . . . . . 64 Spontaneous activity from the lateral line . . . . . 64 Evoked activity from the lateral line . 69 Heart activity. . . . . . . . . . . . . 69 Hypoxia experiments. . . . . . . . . . . . . 7O TABLE OF CONTENTS - Continued Spontaneous activity from the lateral line . . . . Evoked activity from the lateral line Heart activity. . . . . . . . . . . . Asphyxia experiments . . . . . . Spontaneous activity from the lateral line . . . Evoked activity from the lateral line Heart activity. . . . . . . . . . . . Cyanide experiments. . . . . . Spontaneous activity from the lateral line . . . . Evoked activity from the lateral .line Heart activity. . . . . . . . . . . . DISCUSSION . . . . . . . . . . . . . . . . . . . . . DDT Experiments . . . . . . . . . . . . . . . . Hypoxia Experiments . . . . . . . . . . . . . . Asphyxia Experiments. . . . . . . . . . . . . . Cyanide Experiments . . . . . . . . . . . . . . LITERATURE CITED . . . . . . . . . . . . . . . . . . iv Page 106 108 109 115 119 -- - 11-1.;— FIGURE 1 N .p. 5. 6. oo 10. 11. 12. LIST OF FIGURES Diagram of experimental fish chamber, head tank, oxygan metering equipment, and toxicant metering system . . . . . . . . . . . . . . . . . . . . . Electrode apparatus used for recording neural activity from lateral—line nerve in rainbow trout. . . . . . . . . . . . . . . . . . . . . . Block diagram of instrumentation used for record- ing electrical activity from the heart and lateral-line nerve . . . . . . . . . . . . . . . Secured fish showing position of ECG and lateral- ling nerve electrodes. . . . . . . . . . . . . . Entire experimental setup. . . . . . . . . . . . Spontaneous lateral-line activity in control fish demonstrating reduced frequency upon pro- gressively cutting the nerve . . . . . . . . . Examples of various evoked reSponses produced by stimulating the lateral—line . . . . . . . . . . Typical electrocardiogram (ECG) from rainbow trout using a unipolar electrode . . . . . . . . Effect of intravenous injection of DDT on Spon- taneous activity recorded from the lateral-line nerve. . . . . . . . . . . . . . . . . . . . . . Effect of lowered oxygen tension in water on heart rate . . . . . . . . . . . . . . . . . . . Examples of ECG changes during hypoxia . . . . . Effect of asphyxiation on Spontaneous and evoked neural discharge from lateral—line nerve . . . . Page 18 25 57 41 52 55 61 67 75 77 81 LIST OF FIGURES - Continued FIGURE 15. Effect of 4 ppm KCN on spontaneous and neural discharge from the lateral-line 14. Effect of 1 ppm KCN on Spontaneous and neural discharge from the lateral-line evoked nerve. evoked nerve. 15. Effect of 0.5 ppm KCN on Spontaneous and evoked neural discharge from the lateral-line nerve . 16. Effect of 1 ppm KCN exposure on Spontaneous and evoked neural discharge from the lateral-line nerve................. o a o 17. Relationship between Spontaneous and evoked neural activity during asPhyxia and cyanide exposure. . . . . . . . . . . . . . . . 18. Heart rate effects during exposure of fish preparations to 4 ppm KCN . . . . . . . 19. Heart rate effects during exposure of fish preparations to 1 ppm KCN . . . . . . . 20. Heart rate effects during exposure of fish preparations to 0.5 ppm KCN . . . . . . vi 0 Page 86 88 90 95 96 99 101 105 INTRODUCTION Studies in the past which have been concerned with effects of pollution stress upon physiological changes in fish species have largely ignored effects of toxic pollutants upon functional changes in the nervous system. This is un— fortunate since a very large number of toxic substances are recognized as Specific nervous system poisons. In addition to Specific neuro-toxins there are a number of chemicals not normally considered to be neurotoxic which can alter physio- logical processes within the body in such a manner as to have profound secondary effects upon the nervous system. Because the nervous system is extremely sensitive to changes in the internal environment of the body and because it is unparalleled in its role of immediate usefulness to the animal it is not surprising that a large variety of sub- stances can cause severe disability or even death by secondarily affecting the nervous system. It is believed that a more detailed understanding of neural mechanisms in fish, coupled with knowledge of effects of various toxic substances associated with pollution are necessary preliminaries for understanding the complexity of -1:.-‘r —o QMmmo nummU no 825024 0.” 06¢ 00¢ eon - P b n - n - ION I .av . ‘ . I ‘ . . ‘ I :69 I C I . ‘ I 0 .ea COIOII'IIOIIQIIIOSII < 4 . . a UIIIIQIIIIIIIOIIDIII . a u D u IIIJIIOIDIIIIIIIIIIIIII o d d 4 (I --. :— HDHVHOSIG TVHQHN TVILINI d0 lNHDHQd 91 initial value. Fish exposed to 0-3 ppm of cyanide (Figure 115) éiixi not react as fast to the chemical as with levels ‘Df 3— Eppm and 4 ppm. Fish required nearly 400 ug/g of cyanide before the spontaneous activity from the lateral line fell to 50%, and after exposure to 700 ug/g of the poison the a<=tlli—\Iity was still at 40%. Figure 16 (top) shows oscillo— scz<>l;>ee traces of Spontaneous activity in one fish after e3£5ure to 1 ppm KCN. For this particular fish approximately 1£3(:) LLg KCN per gram of fish passed over the gills per hour. Evoked activity from the lateral line. The tOp lines (dashed) in Figures 15, 14, and 15 correspond to the evoked acz‘lzivity measurements after exposure of fish preparations to tklfia same three concentrations of cyanide. In every case the e“’<3}o nmmmo ammmam mon