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Last modified
7/14/2009 5:01:47 PM
Creation date
5/20/2009 5:15:01 PM
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UCREFRP
UCREFRP Catalog Number
9357
Author
Beyers, D. W. and M. S. Farmer
Title
Effects of Copper on olfaction of Colorado Pikeminnow
USFW Year
2001
USFW - Doc Type
Environmental Toxicology and Chemistry
Copyright Material
YES
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<br />910 <br /> <br />Environ. Toxicol. Chern. 20,2001 <br /> <br />1.0 <br /> <br /> <br />Q) <br />II) <br />5 0.8 <br />0- <br />Il) <br />& 0.6 <br />'+- <br />o <br />>- 0.4 <br />~ <br />:.a <br />ro 0.2 <br />.0 <br />o <br />.... <br />a.. 0.0 <br />Control 30 100 <br /> <br />Copper Concentration (.ug/L) <br /> <br />o <br /> <br />300 <br /> <br />Fig. 1. Probability of response to skin homogenate for Colorado <br />pikeminnow exposed to copper for 24 (circles) or 96 h (squares). The <br />mean response for all replicates at each exposure concentration is <br />shown. Probability 1 = response; 0 = no response. <br /> <br />fLg/L total copper; EC50s were 43.3 (28.5, 69.0) and 56.0 <br />(39.3, 86.6) fLg/L total copper, respectively. Comparing these <br />estimates with total copper concentrations in the Yampa River <br />(Fig. 2) revealed that the 24-h EC1 was equaled or exceeded <br />by about 52% of the field samples. The 96-h EC1 was equaled <br />or exceeded by about 14% of the samples. For dissolved cop- <br />per, the 24- and 96-h EC1s were equaled or exceeded by about <br />57 and 2% of field samples, respectively. The EC50 values <br />were approached or exceeded on one or two occasions during <br />the 17 -year period of record. <br /> <br />Scanning electron microscopy <br /> <br />The SEM surveys always detected one or more ciliated <br />receptor cells in control fish but did not detect receptor cells <br />immediately after exposure in fish in the other copper treat- <br />ments examined (Table 3). Observations confirmed that Col- <br />orado pikeminnow regenerated olfactory receptor cells after <br />96-h exposure to 60.0 fLg/L copper. Ciliated receptor cells were <br />detected in the olfactory epithelium of all three fish from this <br />experimental treatment after the 14-d recovery period. <br /> <br />DISCUSSION <br /> <br />Mechanism for variable sensitivity <br /> <br />We exposed Colorado pikeminnow to a gradient of copper <br />concentrations and evaluated the influence on olfaction by <br /> <br />Table 2. Results of behavioral assays after exposure to copper for <br />24 or 96 h or after a 14-d recovery period; values are number of <br />positive behavioral responses/replicates assayed <br /> <br />24-h exposure 96-h exposure 14-d recoverya <br />Concen- Concen- Concen- Positive <br />tration Positive tration Positive tration re- <br />(fLg/L) responses (fLg/L) responses (fLg/L ) sponses <br /><lOb 10/10 <lOb 10/10 <lOb 9/9 <br />16.6 5/9 15.0 10/10 15.0 8/9 <br />33.3 6/10 30.0 8/9 30.0 9/9 <br />66.5 4/10 60.0 5/10 60.0 8/9 <br />133 2/10 120 0/6 NDc ND <br />266 0/10 <br /> <br />a Fish were held in control water for 14 d following 96-h exposure <br />to copper concentrations. <br />b Control. <br />c ND = not determined because few fish recovered from copper <br />exposure. <br /> <br />D.W. Beyers and M.S. Farmer <br /> <br /> 80 <br /> 70 <br /> 60 <br /> 50 <br /> 40 <br /> 30 <br />>- 20 <br />(,) <br />c <br />Q) 10 <br />:J <br />0" 0 <br />~ <br />u.. <br />+-' 80 <br />c <br />Q) <br />(,) 70 <br />.... <br />Q) <br />a.. 60 <br /> 50 <br /> 40 <br /> 30 <br /> 20 <br /> 10 <br /> <br />Total Copper <br /> <br /> <br />. <br /> <br />Dissolved Copper <br /> <br /> <br />10 15 20 25 30 35 40 45 50 55 60 <br />Concentration (f.lg/L) <br /> <br />Fig. 2. Frequency of observation of copper concentrations in the Yam- <br />pa River near Maybell, CO, USA, for the period of record from <br />September 1974 to September 1991 (n = 29 for total copper, 66 for <br />dissolved copper). Histograms represent number of observations less <br />than or equal to the label value in the interval between each category. <br />BD = below detection. <br /> <br />challenging fish to detect and respond to a skin homogenate <br />assumed to contain fright pheromone and by determining pres- <br />ence or absence of ciliated receptor cells in exposed fish. In <br />general, olfactory ability declined with increasing copper con- <br />centration. However, an unexpected result was that the re- <br />sponse to copper varied with duration of exposure. For copper <br />concentrations less than 66 fLg/L, olfaction was more sensitive <br />to exposure at 24 h than at 96 h. This response is inconsistent <br />with the general principle of toxicology that, for a given con- <br /> <br />Table 3. Results of scanning electron microscopy examinations after <br />exposure to copper for 24 or 96 h or after a 14-d recovery period; <br />values are number of fish with one or more ciliated receptor cells/ <br />fish examined <br /> <br />24-h exposure 96-h exposure 14-d recoverya <br />Concen- Concen- Concen- <br />tration Receptors tration Receptors tration Receptors <br />(fLg/L) detected (fLg/L) detected (fLg/L) detected <br /><lOb 3/3 <lOb 3/3 <lOb 3/3 <br />266 0/3 60.0 0/3 60.0 3/3 <br /> 120 0/3 NDc ND <br /> <br />a Fish were held in control water for 14 d following 96-h exposure <br />to copper concentrations. <br />b Control. <br />c ND = not determined because few fish recovered from copper <br />exposure. <br />
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