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Distribution, abundance and overwinter survival of young-of-the-year common carp in a ... PDF

140 Pages·2012·9.56 MB·English
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Distribution, abundance and overwinter survival of young-of-the-year common carp in a 1   Midwestern watershed 2   3   A THESIS 4   SUBMITTED TO THE FACULTY OF THE GRADUATE SCHOOL 5   OF THE UNIVERSITY OF MINNESOTA BY 6   7   Jacob B. Osborne 8   9   IN PARTIAL FULFILLMENT OF THE REQUIREMENTS 10   FOR THE DEGREE OF 11   MASTER OF SCIENCE 12   13   Peter W. Sorensen, Advisor 14   15   March, 2012 16   17   18   19   20   21   22   23   24   25   26   27   28   29   30   31   32 33   34   35   36   37   38   39   40   41   42   43   44   45   Copyright 2012 by 46   Jacob B. Osborne 47   48   All rights reserved 49   50   51   52   53   54   55   56   57   58   59   60   61 Acknowledgements I am grateful to many people and organizations for making possible my graduate experience and research. My advisor, Dr. Peter Sorensen, provided valuable insights into the scientific and writing processes and ensured that I was fully funded. I received funding from the National Science Foundation through the Introduced Species and Genotypes Integrated Graduate Education Research and Traineeship (ISG-IGERT) as well as from the Minnesota Environment and Natural Resources Trust Fund and the Ramsey-Washington Metro Watershed District (RWMWD). Dr. David Andow and Dr. Przemek Bajer served on my committee and Dr. Bajer also provided guidance on how to conduct the mark-recapture efforts described in Study 2 of Chapter 2, served as an otolith reader for Study 2 of Chapter 2, and collected the winter dissolved oxygen data reported in Table 2 of Chapter 2. Dr. Christopher Chizinski collected the data reported in Study 1 of Chapter 2 and Justine Koch conducted the 2011 mark-recapture effort reported in Study 2 of Chapter 2. Dr. Hangkyo Lim and Dr. Haude Leveseque started and supervised much of the lab work presented in appendices 4, 5 and 6. Special thanks to Justin Silbernagel for helping with long days of trap-netting and electro-fishing for Study 2 in Chapter 2. Jordan Wein also assisted greatly with boat electro-fishing in that study. Brett Miller and Mary Headrick provided valuable logistical support and Mary also served as an otolith reader for Study 2 in Chapter 2. Special thanks to the Olson family in Maplewood, MN for use of their boat access on Casey Lake; electro-fishing probably would have been impossible without it. Thanks also to all of the volunteers, whose names are too smudged on my data sheets for me to acknowledge them specifically, who assisted with fieldwork. Assistance with animal care for fishes used in laboratory experiments was provided by several undergraduates, including Chris Johnson, Brian Moe, Eric Sanft and Elizabeth Fox. Jay Maher also provided invaluable assistance coping with technical difficulties related to the aquaculture facilities. Finally, I would like to thank my family, especially my girlfriend, Marta Ribera, who have been with me through the highs and lows of this process. Their unending support has made this possible. i Abstract The common carp (Cyprinus carpio) is one of the most widespread and damaging invasive fishes in North America, yet little is known about its early life history. This paper reports the results of two studies which tested the hypothesis that shallow lakes prone to winter hypoxia (i.e. unstable lakes) serve as nurseries for common carp in interconnected lake systems while lakes that do not experience winterkill (i.e. stable lakes) do not function as nurseries. Six lakes in an interconnected lake system in south- central Minnesota (four stable and two unstable) were sampled using trap-nets in June- August of 2009, 2010 and 2011 and in all three years age-0 carp were captured only in the two unstable lakes. These surveys also revealed that the fish communities in stable lakes were dominated by bluegill sunfish and largemouth bass, species which did not occur naturally in the unstable lakes. Mark-recapture and ageing studies conducted in 2010 in the two carp nurseries indicated that there were ~13,000 age-0 carp in Casey Lake and ~35,000 age-0 carp in Markham Lake. Additional mark-recapture efforts the following summer indicated that ~33% of those fish survived their first winter in Casey Lake while ~4% survived in Markham Lake. Independent trap-net and electro-fishing surveys in the nursery lakes in 2010 revealed that their fish communities were dominated by shorter length classes of hypoxia-tolerant species. Implications of these results for management of nuisance carp populations in interconnected lake systems in North America are discussed. ii Table of Contents Acknowledgements.............................................................................................................i   Abstract..........................................................................................................................................................ii   Table  of  Contents..............................................................................................................iii   List  of  Tables......................................................................................................................iv   List  of  Figures......................................................................................................................v   Chapter  1:  Literature  Review..............................................................................................1   The  distribution  of  juvenile  fishes  in  temperate  lakes  of  North  America...................2   Common  carp  in  temperate  regions  .............................................................................3   Biogeography.............................................................................................................3   General  biology..........................................................................................................3   Management.............................................................................................................4   Life  history.................................................................................................................5   Distribution  of  juvenile  carp......................................................................................6   Factors  contributing  to  the  invasiveness  of  carp.......................................................7   Study  overview..........................................................................................................8   Chapter  2:  Distribution,  abundance  and  overwinter  survival  of  young-­‐of-­‐the-­‐year  carp  in   a  Midwestern  watershed..................................................................................................10   Summary......................................................................................................................11   Introduction.................................................................................................................12   Methods.......................................................................................................................13   Results..........................................................................................................................19   Discussion.....................................................................................................................21   Tables...........................................................................................................................26   Figures..........................................................................................................................31   References...................................................................................................................42   Appendix 1: Tabular summaries of mark-recapture data and the population estimates reported in Chapter 2.........................................................................................................52 iii Appendix 2: Tabular summaries of mark-recapture data and population estimates of other fish species inhabiting carp nursery lakes in 2010.............................................................57 Appendix 3: Comparison of the efficiency of three survey techniques for sampling young-of-the-year carp in nursery lakes............................................................................68 Appendix 4: Experiments investigating the potential use of food odors to facilitate trapping of young-of-the-year and juvenile common carp................................................71 Appendix 5: Experiments investigating the potential use of pheromones to facilitate trapping of young-of-the-year and juvenile common carp ...............................................93 Appendix 6: Amino acid release profiles of several fishes found in the North American Midwest............................................................................................................................100 Appendix 7: Implications of the results of Chapter 2 for ecological risk analysis in watersheds containing potential common carp nursery habitat.......................................127 Appendix 8: Fishes captured in the stream below Markham Lake.........................................129     iv List of Tables 1   Table 1. Organization of the studies described in this paper………………………26 2   3   Table 2. Descriptive information about study lakes in the Phalen Chain………….27 4   5   Table 3. Fish assemblage in the Phalen Chain …………………………………….28 6   7   Table 4. Trap-net catches of fishes in study lakes in the Phalen Chain………........29 8   9   Table 5. Abundance estimates of age-0 carp in nursery lakes in 2010 and age-1 carp 10   in nursery lakes in 2011 …………………………………………………………...30 11   12   13   14   15   16   17   18   19   20   21   22   23   24   25   26   27   28   29   30   31   32   33   34   35   36   37   38   v List of Figures 39   Figure 1. Map of the Phalen Chain near St. Paul, MN. …………………………...31 40   41   Figure 2. Catches of carp <100mm throughout the Phalen Chain.....……………..32 42   43   Figure 3. Length distribution of carp in Casey Lake in 2010…………..................33 44   45   Figure 4. Length distribution of carp in Markham Lake in 2010……....................34 46   47   Figure 5. Length distribution of carp in Casey Lake in 2011…………..................35 48   49   Figure 6. Length distribution of carp in Markham Lake in 2011……....................36 50   51   Figure 7. Fish communities in carp nursery lakes in 2010………………………..37 52   53   Figure 8. Length distributions of all species captured in Casey Lake in trap-net 54   surveys in 2010…………………………………………………………………....38 55   56   Figure 9. Length distributions of all species captured in Casey Lake in electro- 57   fishing surveys in 2010..…………………………………………………………..39 58   59   Figure 10. Length distributions of all species captured in Markham Lake in trap-net 60   surveys in 2010…………………………………………………..………………..40 61   62   Figure 11. Length distributions of all species captured in Markham Lake in electro- 63   fishing surveys in 2010..…………………………………………………………..41 64   65   66   67   68   69   70   71   72   73   74   75   76   vi 77   78   79   80   81   82   83   84   85   86   87   88   89   90   91   Chapter 1: A literature review 92   93   94   95   96   97   98   99   100   101   102   103   104   105   106   107   1 The distribution of juvenile fishes in temperate lakes of North America 108   Temperate lakes are dynamic environments in which physiochemical and 109   biological conditions vary both spatially and temporally. This heterogeneity results in a 110   diverse range of potential habitats for juvenile fishes lakes (Schindler and Scheuerell 111   2002). However, the distribution of juvenile fishes is often restricted to a narrow subset 112   of these habitats, even if other life stages of the same species utilize additional areas. 113   Habitats that support relatively high densities of juvenile fishes are often referred to as 114   ‘rearing’ or ‘nursery’ habitats (Jones et al. 2003) and are generally assumed to ultimately 115   contribute disproportionately more individuals to the adult population than are 116   contributed by adjacent habitats (Beck et al. 2001). 117   Littoral habitats function as nurseries for many lacustrine fishes in North 118   America. In a review of nursery habitats used by fishes inhabiting the Laurentian Great 119   Lakes, Lane et al. (1996) reported that juveniles of most of the 102 species for which data 120   were available were most abundant in water shallower than 2m and were generally 121   associated with aquatic vegetation over sandy or silty substrate. The authors suggested 122   this pattern was because aquatic vegetation provides a physical refuge from predators and 123   also supports invertebrates on which juvenile fishes may feed (Herdendorf et al. 1986; 124   Becker, 1983). Similar patterns have also been documented in smaller lakes. Werner and 125   Hall (1988) studied habitat use of bluegill sunfish (Lepomis macrochirus) in four 126   Michican lakes ranging in area from 50 to 2000 ha and reported an ontogenetic habitat 127   shift from the limnetic zone, where bluegill larvae were observed feeding for several 128   weeks after hatching, to the vegetated littoral zone, where feeding continued for the rest 129   of the juvenile period. The authors hypothesized that this shift, which was consistent 130   across all four study lakes, was due to reduced risk of predation for the young fish in 131   vegetation compared to open water habitats. Non-vegetated habitats can also function as 132   nurseries. Olson et al. (2003) studied habitat use of young-of-the-year smallmouth bass 133   (Micropterus dolomeiu) in New York lakes and observed that they were found primarily 134   in cobble habitats that lacked vegetation, in spite of the availability of vegetated habitats. 135   Based on subsequent lab experiments the authors concluded that juvenile smallmouth 136   bass were both less vulnerable to predators and also more efficient at foraging in cobble 137   2

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Assistance with animal care for fishes used in laboratory experiments was The common carp (Cyprinus carpio) is one of the most widespread and .. However, the connectivity found in these systems allows more mobile sabotage using water level manipulation has also been attempted (Shields
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