Abstract
During June and July 2012, Buffalo Pound Lake and Blackstrap Lake in Saskatchewan, Canada were visited biweekly and surveyed for sick and dying fish. During this investigation, 2 fish kills were identified. Buffalo Pound experienced a large die-off of yellow perch (
In July 2011, thousands of dead fish, mainly small yellow perch (
Buffalo Pound Lake (50°39′N 105°30′W) and Blackstrap Lake (51°47′N 106°25′W) are man-made reservoirs, which are part of the Qu’Appelle drainage system in southern Saskatchewan. Both lakes are shallow (depth 5–9 m), exhibit little to no thermal stratification, are eutrophic, and have experienced fish kills in the past. In June and July 2012, these lakes were monitored for fish kills once every 2 weeks during daylight hours, or once per week when die-offs were occurring. The length of each reservoir was explored by boat in order to survey for dead and dying fish.
Dead and sick fish were examined for lesions, and a subset of fish was collected by dip net and subsequently euthanized in a water bath supersaturated with tricaine methanesulfonate (MS-222) a buffered with sodium hydroxide. Complete necropsies were conducted on site, and representative sections of all major tissues were fixed in 10% neutral buffered formalin, decalcified with 5% formic acid, trimmed into 5-µm-thick sections, and stained with hematoxylin and eosin for routine histologic examination. A subset of slides was additionally stained with Brown and Brenn (Gram stain). Unstained wet mounts of external lesions were examined under light microscope.
Fresh samples of gill and/or skin, kidney, spleen, and less frequently heart and liver, were aseptically cultured onto blood agar, MacConkey agar, and
Colonies that were morphologically consistent with
Genomic DNA was isolated from 2 isolates from each lake, which were morphologically and biochemically compatible with
Based on field observations and reports made by members of the public, Buffalo Pound Lake experienced a large fish die-off during June 8–19. Yellow perch were primarily affected, but small numbers of fathead minnows (
In excess of 50 fish were examined for external lesions, all of which consistently had multifocal cutaneous petechial hemorrhages and erosion and ulceration of the skin. Of these, 8 moribund yellow perch (mean fork length 13.7 cm) and 1 male fathead minnow (fork length 3 cm) were collected for necropsy and bacterial culture. Of the yellow perch collected, 2 were female, 1 was male, and 5 were undetermined. Seven out of 8 (88%) yellow perch had areas of pale discoloration on the body wall (Fig. 1), corresponding to loss of surface scales, erosion of the skin, degeneration of the underlying musculature, and infiltration of Gram-negative filamentous bacteria. One yellow perch had mild necrotizing branchiitis (Fig. 2). In 50% (4/8) of yellow perch, there were large parasitic pseudocysts and free myxospores distributed throughout the spinal cord and brain, consistent with

Yellow perch (

Body wall; yellow perch (
Based on field observations and reports made by the public, Blackstrap Lake experienced a large die-off of lake whitefish (
In excess of 50 fish from Blackstrap Lake were examined for external lesions, all of which were consistently covered by large amounts of mucous and had multifocal cutaneous hemorrhages; severe gill necrosis was present in the majority of fish examined. Of these, 7 moribund and 1 dead white fish were collected for necropsy and bacterial culture; 6 males and 2 females, with an average weight of 2.15 kg and fork length of 48 cm. All fish were covered by an excessive amount of mucous, and the base of the fins was erythematous. In 88% (7/8) of fish collected, up to 25% of the gill filaments were eroded and replaced by brown necrotic debris, hemorrhage, and stacked aggregates of filamentous Gram-negative bacteria, small Gram-negative rods, and few algae (Figs. 3, 4); motile filamentous bacteria were noted on wet mount preparations. In 100% (8/8) of fish, the epicardium was diffusely covered by 1-mm-diameter white nodules, which corresponded to metacercariae surrounded by granulomatous inflammation. In 100% (8/8) of whitefish, there was marked lymphoid depletion in the spleen, and melanomacrophage centers were abundant.

Gills; lake whitefish (

Gills; lake whitefish (
The commercial rapid identification system identified
The species selectivity and the duration of the fish kills observed in the Buffalo Pound and Blackstrap fish kills was suggestive of environmental perturbation with subsequent opportunistic infection.
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Identifying bacterial disease in wild fish is often complicated by rapid autolysis and overgrowth by saprophytic bacteria. However, these issues were circumvented in the present study by actively surveying lakes and collecting live fish, which exhibited lesions similar to those present on dead fish.
8
Based on postmortem and histologic findings, in combination with bacteriologic results, both fish kills were attributed to an outbreak of
In many cases, columnaris disease is complicated by secondary bacterial and fungal infections, which can likely be attributed to a combination of immunosuppression and damage to the natural barrier provided by the skin.
4
A mixed infection of
The difference in fish species affected in the Buffalo Pound and Blackstrap die-offs likely reflect differences in underlying factors that predisposed fish to columnaris disease. In Buffalo Pound, oxygen levels did not appear to be depleted because large fish were not affected, ambient air temperature was cool, and there appeared to be adequate surface wind mixing based on field observations. A fishery stock assessment, which was conducted at the same time as the fish kill, revealed that the yellow perch population in Buffalo Pound was extremely abundant based on catch per unit effort (Jennifer Merkowski, personal communication, 2012). This is of particular interest because not only does high stocking density enhance horizontal transmission of bacteria, but also it acts as a stressor, predisposing yellow perch to columnaris disease. 15 An outbreak of columnaris disease occurred previously in white suckers in Buffalo Pound Lake in June 1972; however, factors that may have triggered the outbreak were not discussed. 21
Based on field observations and the fact that large fish were targeted during the Blackstrap fish kill, the whitefish mortality was probably due in part to increasing water temperatures and reduced oxygen availability. The epicardial metacercaria in whitefish from Blackstrap is consistent with
Although cyanobacteria are known to reside in nutrient-rich lakes, microcystin toxicity was considered unlikely in the current study because algal blooms were not observed, and fish did not have characteristic lesions.
7
Most fish kills caused by agricultural and industrial toxins involve several different species of fish and occur within a short time frame,
12
neither of which were features of die-offs in the present study. Toxic levels of hydrogen sulfide and ammonia were also considered an unlikely cause of mortality due to an absence of typical lesions.
10
In conclusion, the current study identified
Footnotes
Acknowledgements
The authors would like to thank Saskatchewan Ministry of Environment staff for their assistance in collecting yellow perch in summer 2011. The authors would also like to thank the Animal Health Centre, Plant and Animal Health Branch, BC Ministry of Agriculture, Abbotsford, British Columbia, for performing the polymerase chain reaction assays, and Dr. Frederick A. Leighton for reviewing earlier versions of this article.
a.
Syndel Laboratories Ltd., Qualicum Beach, British Columbia, Canada.
b.
EMD Bioscience Inc., La Jolla, CA.
c.
Sigma-Aldrich, St. Louis, MO.
d.
DrySlide oxidase slides, BD Diagnostic Systems, Sparks, MD.
e.
API20E rapid identification system, bioMérieux Canada Inc., St. Laurent, Quebec, Canada.
f.
Ricca Chemical Co., Arlington, TX.
g.
DNeasy blood & tissue, Qiagen GmbH, Hilden, Germany.
Declaration of conflicting interests
The author(s) declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.
Funding
The author(s) disclosed receipt of the following financial support for the research, authorship, and/or publication of this article: Funding for the study was provided by the Saskatchewan Fish and Wildlife Development Fund.
