Outbreak ofCleidodiscusin juvenile black crappies (Pomoxis nigromaculatus) and bath treatment with praziquantel

2017 ◽  
Vol 40 (11) ◽  
pp. 1737-1739 ◽  
Author(s):  
C Bader ◽  
J Jesudoss Chelladurai ◽  
K Thompson ◽  
D Starling ◽  
M T Brewer
Keyword(s):  
Pomoxis Nigromaculatus

Movement Patterns of Adult Black Crappie,Pomoxis nigromaculatus, in Brant Lake, South Dakota

1992 ◽  
Vol 7 (2) ◽  
pp. 137-147 ◽  
Author(s):  
Christopher S. Guy ◽  
Robert M. Neumann ◽  
David W. Willis
Keyword(s):  
South Dakota ◽  
Movement Patterns ◽  
Pomoxis Nigromaculatus

Feeding Biology of the Black Crappie, Pomoxis nigromaculatus

1968 ◽  
Vol 25 (2) ◽  
pp. 285-297 ◽  
Author(s):  
Allen Keast
Keyword(s):  
Body Length ◽  
Micropterus Salmoides ◽  
Lepomis Macrochirus ◽  
Insect Larvae ◽  
Progressive Change ◽  
Pomoxis Nigromaculatus ◽  
Feeding Biology ◽  
Ambloplites Rupestris ◽  
Gill Raker ◽  
Diptera Larvae

In Lake Opinicon, Ontario, the diet of the black crappie, Pomoxis nigromaculatus, undergoes a progressive change from one in which planktonic Crustacea and small-bodied Diptera larvae predominate (in fish of body length from about 60 to 115 mm), to a diet of insect larvae and fish (in fish 160–240 mm). Most food items prove to be midwater forms and the Diptera larvae are almost entirely Chaoborus and Procladius, which are free-swimming in the water column at night.An unusual feature is the prolonged nature of the Cladocera-Copepoda eating phase, which continues into year III and to a body length of about 160 mm. Gill-raker counts show P. nigromaculatus to have a specialized screen with 25–29 rakers on the first arch. In this it differs from cohabiting centrarchids in Lake Opinicon, Ambloplites rupestris, Micropterus salmoides, and Lepomis macrochirus, in which the rakers on the first arch number only 8–12. In these species plankton feeding is restricted to the earlier stages.

Balancing Fisheries Management and Water Uses for Impounded River Systems

2008 ◽  
Keyword(s):  
Micropterus Salmoides ◽  
Lepomis Macrochirus ◽  
Northern Pike ◽  
Smallmouth Bass ◽  
Biological Information ◽  
Specific Work ◽  
Pomoxis Nigromaculatus ◽  
Management Responsibility ◽  
Species Specific ◽  
Individualized Management

<em>Abstract</em>.—In the 1990s, the Minnesota Department of Natural Resources, Fisheries Section, responded to angler requests to manage the state’s waters on a more individual basis. Individual waters management often included the development of length-based regulations and/or bag limit reductions. Although the move towards individual waters management was biologically sound and by and large supported by anglers, it also created some problems. By the late 1990s, there were more than 150 specialized regulations for northern pike <em>Esox lucius</em>, walleyes <em>Sander vitreus</em>, largemouth bass <em>Micropterus salmoides</em>, smallmouth bass <em>M. dolomieu</em>, black crappies <em>Pomoxis nigromaculatus</em>, white crappies <em>P. annularis</em>, and bluegills <em>Lepomis macrochirus</em>. With management responsibility on more than 6,000 lakes, it became clear that some type of regulation streamlining or standardization was needed. Public input meetings indicated that anglers wanted continued individualized management of lakes and the opportunity to catch quality-sized fish but were concerned about the growing number and complexity of regulations. In response, species-specific work groups consisting of research and management biologists were formed to identify what biological information was available and what was needed to develop a set of species-specific regulations. Standardized regulations were developed for northern pike, walleyes, largemouth and smallmouth bass, bluegills, and both species of crappies. We discuss the development of the standardized regulations for crappies, where size and bag limit categories were established based on growth and natural mortality targets. Future field collections will be required to measure the effectiveness of these regulations.

Recovery and confirmation of Edwardsiella piscicida from a black crappie Pomoxis nigromaculatus (Lesueur, 1829)

2019 ◽  
Vol 42 (10) ◽  
pp. 1457-1461
Author(s):  
Matt J. Griffin ◽  
B. Denise Petty ◽  
Cynthia Ware ◽  
Susan B. Fogelson
Keyword(s):  
Pomoxis Nigromaculatus ◽  
Edwardsiella Piscicida

Observations on the glochidia of Lampsilis radiata (Gmelin) infesting yellow perch, Perca flavescens (Mitchill) in the Bay of Quinte, Lake Ontario

1969 ◽  
Vol 47 (4) ◽  
pp. 705-712 ◽  
Author(s):  
Shibru Tedla ◽  
C. H. Fernando
Keyword(s):  
Yellow Perch ◽  
White Perch ◽  
Micropterus Salmoides ◽  
Perca Flavescens ◽  
Lake Ontario ◽  
Smallmouth Bass ◽  
Lepomis Gibbosus ◽  
Experimental Conditions ◽  
Pomoxis Nigromaculatus ◽  
Rock Bass

Analysis of incidence and intensity of infestation of yellow perch, Perca flavescens (Mitchill), by the glochidia of Lampsilis radiata from weekly samples from May to September and single samples in October and November indicate that the two subspecies, Lampsilis radiata radiata and Lampsilis radiata siliquoidea, shed their glochidia in late spring and throughout the summer in the Bay of Quinte, Lake Ontario. Smaller fish are more heavily infested with these glochidia than larger ones. About 50% of the preparasitic glochidia of Lampsilis radiata siliquoidea survived for 12, 70, and 120 h at 20°, 12°, and 10 °C respectively. The parasitic period of the glochidia of L. r. siliquoidea on yellow perch under experimental conditions was 50 days at 15 °C from the May infestation. Yellow perch carried the glochidia for a longer period from an August infestation. All the glochidia recovered 50 days after infestation, both from May and August infestations, had undergone metamorphosis. There was no difference in the degrees of infestation of the different species of fish used in our experiments. Pumpkinseed, Lepomis gibbosus (Linnaeus); rock bass, Ambloplites rupestris (Rafinesque); and white perch, Roccus americanus (Gmelin) lost their infestations in a week. Presumably no metamorphosis took place under these conditions. Black crappie, Pomoxis nigromaculatus (LeSueur); largemouth bass, Micropterus salmoides (Lacepede), smallmouth bass, M. dolomieui Lacepede: and yellow perch carried the infestation till they were killed 20 days later. There was no relationship between the numbers of glochidia (Lampsilis radiata) and copepods, (Ergasilus confusus Bere) on naturally infested yellow perch, nor on rock bass, smallmouth bass, and pumpkinseed which harbored Ergasilus spp. naturally and which were infested with the glochidia of L. r. siliquoidea experimentally.

Experimental Acidification of Little Rock Lake, Wisconsin: Chemical and Biological Changes over the pH Range 6.1 to 4.7

1993 ◽  
Vol 50 (5) ◽  
pp. 1101-1121 ◽  
Author(s):  
P. L. Brezonik ◽  
J. G. Eaton ◽  
T. M. Frost ◽  
P. J. Garrison ◽  
T. K. Kratz ◽  
...  
Keyword(s):  
Micropterus Salmoides ◽  
Little Rock ◽  
Pomoxis Nigromaculatus ◽  
Food Web Interactions ◽  
Biological Responses ◽  
Seepage Lake ◽  
Experimental Acidification ◽  
Ph Range ◽  
Ambloplites Rupestris ◽  
Oak Leaves

The two basins of this seepage lake were separated by a vinyl curtain in August 1984 after a year of background studies, and acidification of one basin with H2SO4 began at ice-out in 1985. Chemical and biological responses measured during successive 2-yr periods at pH ~5.6, 5.1, and 4.7 verified some but not all impacts predicted at the outset. Changes in major, minor, and trace ions generally agreed with predictions. Internal alkalinity generation (IAG) increased at lower pH, and sulfate reduction eliminated ~50% of added H2SO4. Sediment cation exchange was important in IAG and acidified surface sediments, possibly diminishing the lake's ability to counteract further H+ inputs. Mass loss of oak leaves was reduced at pH 5.1 (birch leaves at pH 4.7). Population parameters were more sensitive than community measures for plankton. Species composition changed at each pH, especially at pH 4.7. Many changes in zoopiankton and benthos were indirect responses to an algal mat that developed at lower pH or to food web interactions; these were not predicted accurately. Sensitivity of major fishes to lower pH was Ambloplites rupestris > Micropterus salmoides > Pomoxis nigromaculatus > Perca flavescens. Fish production was reduced at pH's above those resulting in population decreases.

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