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<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
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<br />EFFECTS OF COPPER ON OLFACTION OF COLORADO PIKEMINNOW
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<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
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<br />(Received 16 May 2000; Accepted 29 August 2000)
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<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.
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<br />Keywords~Copper
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<br />Colorado pikeminnow
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<br />Olfaction
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<br />,l,
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<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
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<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.
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<br />Behavioral assay
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<br />Scanning electron microscopy
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<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.
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<br />MATERIALS AND METHODS
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<br />Experimental animals
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<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.
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<br />Exposure conditions
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<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
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