Manipulation of ploidy in yellow perch (Perca flavescens) by heat shock, hydrostatic pressure shock, and spermatozoa inactivation

Aquaculture ◽  
1993 ◽  
Vol 110 (3-4) ◽  
pp. 229-242 ◽  
Author(s):  
Jeffrey A. Malison ◽  
Terrence B. Kayes ◽  
James A. Held ◽  
Terence P. Barry ◽  
Clyde H. Amundson
1974 ◽  
Vol 31 (9) ◽  
pp. 1503-1506 ◽  
Author(s):  
Thomas G. Yocom ◽  
Thomas A. Edsall

Fry of lake whitefish (Coregonus clupeaformis) acclimated to 10, 15, and 18 C were exposed to temperatures of 24.5, 25, and 28 C for 1 min and then immediately returned to water at their acclimation temperature, in test tanks containing yearling yellow perch (Perca flavescens). The number of attacks on the fry and the number captured and eaten in 30 min were recorded in separate tests of shocked and unshocked (control) whitefish.Significantly more whitefish were captured per attack (data for shocked and unshocked fry combined) at 15 and 18 C than at 10 C; and shocked fry were significantly more vulnerable to capture by the perch than were unshocked controls.


1993 ◽  
Vol 71 (7-8) ◽  
pp. 361-371 ◽  
Author(s):  
Christine L. Haskin ◽  
Kyriacos A. Athanasiou ◽  
Robert Klebe ◽  
Ivan L. Cameron

Human osteosarcoma cells, MG-63, were exposed to a hydrostatic pressure shock of 4.0 MPa for 20 min. Changes in subcellular distribution of the cytoskeletal elements and heat shock protein 70 (hsp70) were followed by indirect immunofluorescence and by avidin–biotin–peroxidase protocols. During recovery, total cellular RNA was determined and actin and aldolase mRNA content was followed using reverse transcription – polymerase chain reaction techniques. Hydrostatic pressure caused cell rounding (but not cell death), disruption of microtubules, collapse of intermediate filaments to a perinuclear location, collapse of actin stress fibers into globular aggregates in the cytoplasm, and the formation of several large elongated intranuclear actin inclusions. During recovery, the cells flattened, reorganized microtubules, and redistributed intermediate filaments prior to the reappearance of actin stress fibers. At 20 and 60 min following the initiation of hydrostatic pressure, there was increased anti-hsp70 staining at the nuclear membrane and concentration of hsp70 in four to six granules in the nucleus. At 120 min following the hydrostatic pressure, hsp70 showed intense staining in the cytoplasm and hsp70-containing granules in the nucleus disappeared. Cellular RNA decreased during the first 120-min posthydrostatic pressure shock and then recovered to near prehydrostatic pressure treatment levels by 240 min. Actin mRNA abundance, in relation to aldolase mRNA abundance, showed the same temporal pattern of initial decrease, followed by increase as did total RNA. Review of the literature indicated that eukaryotic cells respond to heat shock and to hydrostatic pressure by disruption of the cytoskeletal elements and by similar modifications in genetic expression. In this study, the observed responses of MG-63 cells to a 4-MPa hydrostatic pressure shock was like the reported response of mammalian cells to a 43 °C heat shock.Key words: heat shock response, hydrostatic pressure, cytoskeleton.


2001 ◽  
Vol 63 (1) ◽  
pp. 17-24 ◽  
Author(s):  
Jeffrey A. Malison ◽  
James A. Held ◽  
Lynne S. Weil ◽  
Terrence B. Kayes ◽  
Gary H. Thorgaard

1995 ◽  
Vol 52 (3) ◽  
pp. 464-469 ◽  
Author(s):  
Todd M. Koel ◽  
John J. Peterka

Laboratory-based bioassays were conducted to determine concentrations of sodium-sulfate type salinities that limit the hatching success of several fish species. Survival to hatching (SH) was significantly lower (P < 0.05) in sodium-sulfate type waters from Devils Lake, North Dakota, of ≥ 2400 mg/L total dissolved solids (TDS) than in fresh water of 200 mg/L. In waters of 200, 1150, 2400, 4250, and 6350 mg/L TDS, walleye (Stizostedion vitreum) SH was 41, 38, 7, 1, and 0%; northern pike (Esox lucius) SH was 92, 68, 33, 2, and 0%; yellow perch (Perca flavescens) SH was 88, 70, 73, 0, and 0%; white sucker (Catostomus commersoni) SH was 87, 95, 66, 0, and 0%; common carp (Cyprinus carpio) SH was 71, 69, 49, 63, and 25%.


2003 ◽  
Vol 3 (4) ◽  
pp. 341-346 ◽  
Author(s):  
T DOMITROVIC ◽  
F PALHANO ◽  
C BARJAFIDALGO ◽  
M DEFREITAS ◽  
M ORLANDO ◽  
...  

Aquaculture ◽  
1993 ◽  
Vol 116 (2-3) ◽  
pp. 121-133 ◽  
Author(s):  
Jeffrey A. Malison ◽  
Lynne S. Procarione ◽  
James A. Held ◽  
Terrence B. Kayes ◽  
Clyde H. Amundson

1992 ◽  
Vol 49 (12) ◽  
pp. 2474-2482 ◽  
Author(s):  
Jay A. Nelson ◽  
John J. Magnuson

Little is known about the animals that occupy naturally acidic habitats. To better understand the physiological state of animals from temperate, naturally acidic systems, we compared metabolite stores and meristics of two yellow perch (Perca flavescens) populations in northern Wisconsin. One population originated from a naturally acidic, dystrophic lake (Acid-Lake-Perch, ALP) and had previously been shown to have enhanced tolerance to low pH. The second population came from two nearby interconnected circumneutral, mesotrophic lakes (Neutral-Lake-Perch, NLP). Perch were collected throughout the year to account for seasonal effects and to discern whether patterns of metabolite utilization differed between populations. ALP had smaller livers containing less glycogen and greater muscle glycogen content than NLP. The ALP also had significantly greater liver and visceral lipid contents, and females from this population committed a greater fraction of their body mass to egg production. We interpret these results as indicative of physiological divergence at the population level in yellow perch. These results are discussed as possible products of H+ -driven changes in metabolism and as possible products of different life history strategies between populations. Our results also show that perch living in acidic, dystrophic Wharton Lake are not acid stressed.


1977 ◽  
Vol 34 (10) ◽  
pp. 1774-1783 ◽  
Author(s):  
Lloyd L. Smith Jr.

In an investigation of the commercial fishery of Red Lakes, Minnesota, for the 46-yr period 1930–75, catch statistics were analyzed, and the dynamics of the perch and walleye populations were examined. Mean annual yields of walleye for two statistical periods, 1930–53 and 1954–75, were 309,900 and 245,100 kg, respectively for walleyes, and 96,400 and 109,500 kg for perch. Annual abundance (CPE based on average catches per day per 5-net units of gill nets) varied from 3.8 to 64.6 kg for walleye, and from 2.5 to 34.4 kg for perch. Causes of fluctuations in harvestable stock were directly related to strength of year-classes and to growth rate during the season of capture. Year-class strength was not related to the abundance of parent stock or of potential predators. The respective strengths of year-classes of perch and walleye in the same year were positively correlated (r = 0.859, P < 0.01), and are directly related to climatic factors. Growth rate of walleye in different calendar years varied from +30.7 to −42.2% of mean growth, and that of perch from +13.4 to −8.6% (1941–56). Growing season began in mid-June and was almost over by September 1. Walleye yield could be enhanced by starting harvest July 1 instead of early June. Perch yield could be improved by harvesting small perch. Key words: Percidae, Perca, population dynamics, Stizostedion, long-term yield


1997 ◽  
Vol 54 (8) ◽  
pp. 1903-1915 ◽  
Author(s):  
S A Thayer ◽  
R C Haas ◽  
R D Hunter ◽  
R H Kushler

Zebra mussels (Dreissena polymorpha) in enclosures located in an experimental pond adjacent to Lake St. Clair, Michigan, increased sedimentation rate but had relatively minor effects on percent organic matter and percent nitrogen content of sediment. In contrast, sediment from Lake St. Clair adjacent to zebra mussels was significantly higher in carbon than that 0.5 m away. Zebra mussels increase the nutritional value of surficial sediment and provide greater structural heterogeneity, which is probably more important in causing change among zoobenthos. Zoobenthos and yellow perch (Perca flavescens) diet were dominated by dipteran larvae and leeches. Zoobenthos was significantly different between enclosures with and without zebra mussels. Treatments with zebra mussels had significantly more oligochaetes and tended to have more crustaceans (isopods and amphipods). In June, yellow perch without zebra mussels consumed significantly more zooplankton, and those with mussels had more crustaceans in their diet. Zooplankton density was greater in treatments without zebra mussels. Yellow perch with zebra mussels grew significantly more than those without mussels. Zebra mussels in the enclosures neither reproduced nor were eaten by yellow perch; hence. the observed growth differences were due to indirect effects involving zebra mussel induced changes in benthic structure and biota.


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