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<br />'I . 1 1- <br />"),, () () I r> e V 0'5' C,lf1 d ;- (Ii,! YY/ 2,( <br /> <br />ISETA~/PRESS I <br /> <br />(( <br /> <br />? <br /> <br />Environmental Toxicology and Chemistry, Vol. 20, No.4, pp. 907-912, 2001 <br />@ 2001 SETAC <br />Printed in the USA <br />0730-7268/01 $9.00 + .00 <br /> <br />. <br />l <br /> <br />EFFECTS OF COPPER ON OLFACTION OF COLORADO PIKEMINNOW <br /> <br />I <br />~ <br /> <br />DANIEL W. BEYERS* and MICHAEL S. FARMER <br />Larval Fish Laboratory, Department of Fishery and Wildlife Biology, Colorado State University, Fort Collins, Colorado 80523, USA <br /> <br />(Received 16 May 2000; Accepted 29 August 2000) <br /> <br />Abstract~Effects of copper on olfaction of Colorado pikeminnow (Ptychocheilus lucius) were investigated by exposing fish for <br />24 or 96 h, then evaluating olfactory ability using a behavioral assay and observing olfactory structures using scanning electron <br />microscopy (SEM). The behavioral assay measured a response known as fright reaction. Failure of exposed fish to demonstrate a <br />fright reaction in the presence of skin homogenate assumed to contain fright pheromone was considered evidence of copper-induced <br />loss of olfactory ability. Regression analysis was used to describe the response of fish as a function of copper concentration at <br />each exposure duration. Olfactory ability declined with increasing copper concentration. For copper concentrations less than 66 <br />fLg/L, olfaction was more sensitive to exposure at 24 h than at 96 h. This result suggests that physiological adaptation and recovery <br />of sensory ability occurred despite continuous exposure in the 96-h treatment. Protective mechanisms induced by exposure may <br />have reduced sensitivity to copper by 96 h. Systematic surveys using SEM to detect presence or absence of olfactory receptors <br />confirmed results of behavioral assays. Copper concentrations in one river inhabited by Colorado pikeminnow were compared with <br />effective concentrations estimated by regression. Comparisons suggest that ambient copper concentrations may occasionally inhibit <br />olfaction of wild fish. <br /> <br />Keywords~Copper <br /> <br />Colorado pikeminnow <br /> <br />Olfaction <br /> <br />,l, <br /> <br />INTRODUCTION <br /> <br />The Colorado pikeminnow (Ptychocheilus lucius) is a large <br />cyprinid endemic to the Colorado River Basin, USA [1]. His- <br />torically, the Colorado pikeminnow was widespread in warm- <br />water streams and rivers, but the species was listed as federally <br />endangered in 1967 in response to declining populations [2]. <br />The decline of Colorado pikeminnow is commonly attributed <br />to interactions with introduced fishes, construction of dams, <br />and habitat modification [3,4], but effects of chemical contam- <br />inants are increasingly becoming a concern. An important el- <br />ement of Colorado pikeminnow life history is that natural <br />reproduction is preceded by spawning migrations that may <br />exceed 100 km in length. The means of navigation used by <br />Colorado pikeminnow during migration are unknown, but it <br />has been proposed that olfaction is a critical component of the <br />homing process [1]. Many contaminants are known to disrupt <br />olfaction in fish. Short-term sublethal exposure to copper, lead, <br />mercury, nickel, silver, zinc, extremes of pH, and naphthalene <br />inhibit olfactory ability [5-9]. Olfactory receptors are not pro- <br />tected from contaminant exposure by external membranes but <br />come into direct contact with water-borne solutes. Toxic sub- <br />stances may alter detection of olfactory cues through several <br />modes of action, including damaging organelles and enzyme <br />systems, direct interaction with membrane receptor sites, or <br />masking biologically important chemical signals. <br />The purpose of this investigation was to describe the effect <br />of contaminant exposure on olfactory ability of Colorado <br />pikeminnow. This objective was achieved by exposing Col- <br />orado pikeminnow to sublethal concentrations of copper for <br />24 or 96 h and evaluating olfactory ability using a behavioral <br />assay coupled with observations of olfactory structures using <br /> <br />* To whom correspondence may be addressed <br />(danb@lamar.colostate.edu). <br />Contribution 117, Larval Fish Laboratory, Colorado State Uni- <br />versity, Fort Collins, Colorado, USA. <br /> <br />Behavioral assay <br /> <br />Scanning electron microscopy <br /> <br />scanning electron microscopy (SEM). Advantages of combin- <br />ing the two techniques were that the behavioral assay required <br />study fish to detect, process, and respond to stimuli in an <br />ecologically relevant fashion, and SEM observations provided <br />evidence of related structural changes of olfactory receptors. <br />The behavioral assay used in this investigation measured a <br />response known as fright reaction in Colorado pikeminnow. <br />The fright reaction is a well-known response of Ostariophysan <br />fishes to fright pheromone, which is released from specialized <br />cells in the epidermis when mechanical damage occurs [10,11]. <br />Fright pheromone is detected by olfaction [10,11]. Conse- <br />quently, failure of metal-exposed fish to demonstrate a fright <br />reaction in the presence of the pheromone was considered <br />evidence of a copper-induced loss of olfactory ability. Re- <br />sulting exposure-response relationships were compared with <br />copper concentrations near a Colorado pikeminnow spawning <br />site to evaluate potential for effects on wild fish. <br /> <br />MATERIALS AND METHODS <br /> <br />Experimental animals <br /> <br />Colorado pikeminnow were obtained from Dexter National <br />Fish Hatchery and Technology Center (Dexter, NM, USA). <br />Fish were fed a mixture of live <24-h-old brine shrimp nauplii <br />(Aquarium Products, Glen Burnie, MD, USA) and a com- <br />mercially prepared flake diet (TetraMin@; TetraWerke, Melle, <br />Germany) twice daily. Colorado pikeminnow were 185 d old <br />(after hatching) when studies were started. Total length and <br />wet weight ranged from 25 to 44 mm and 0.14 to 0.68 g, <br />respecti vel y. <br /> <br />Exposure conditions <br /> <br />The 24- and 96-h exposures were conducted following pre- <br />scribed methods for renewal-acute toxicity tests [12]. Six con- <br />centrations were studied for the 24-h exposure (< 10, 16.6, <br />33.3,66.5, 133, and 266 ILg/L copper) and five concentrations <br /> <br />907 <br />