|
The
Influence of Fish Presence on Amphibian Breeding Efforts
in
a Central Illinois Field Experiment
J.
Brian Towey
Department
of Biological Sciences, Eastern Illinois University, Charleston, IL
Introduction
Introduced species
often have negative impacts on populations of native taxa. The presence of
introduced predatory fish may reduce breeding success of native amphibians. A
management strategy of eliminating predatory fish from breeding ponds may
promote native amphibian populations. This study examines amphibian communities
at four neighboring woodland ponds in central Illinois before and after
extermination of introduced fish populations from two of those ponds.
 |
Figure 1. Ambystoma texanum
(Smallmouth salamander) Vermilion County, IL. Photo by C.A.
Phillips |
Methods
Warbler Woods
Nature Preserve is a recently established forest reserve managed by the Illinois
Department of Natural Resources (IDNR). There are four neighboring ponds on the
reserve which are all used by amphibian species as breeding sites. The ponds
have been monitored since May 2000 using screen wire drift fences and pit trap
arrays. Traps are located on both sides of the fence, spaced 7.5 m apart. I
monitored traps every 2 to 3 days throughout the activity season of local
amphibians. I toe-clipped all new animals to indicate the year of initial
capture and released them on the opposite side of the fence.
 |
Figure 2.
Screen wire drift fences. |
Fish Removal
In December 2001,
IDNR officials applied RotenoneTM to ponds B
and C to eliminate the fish species from those two ponds (Ameiurus melas
from pond B and Lepomis machrochirus and L. cyanellus from pond
C). The application appears to have been successful for the eradication of
centrarchids in pond C. However, several live Ameiurus melas have been
noted in pond B since application, though markedly fewer individuals than noted
prior to RotenoneTM application.
 |
 |
|
Figures 3 and
4. RotenoneTM treated ponds. |
Ponds
A - No
history of inhabitation by fish.
B -
Contained introduced Black Bullhead Catfish (Ameiurus melas) until
RotenoneTM application in December 2001.
C -
Contained introduced Bluegill and Green Sunfish (Lepomis machrochirus
and L. cyanellus) until RotenoneTM
application in December 2001.
D - No
history of inhabitation by fish. Ephemeral.
Results
Fisher’s exact
tests by life history stage (Breeding adult / Neonate) and year of capture
revealed differences in Ambystoma texanum numbers between treatment years
at ponds A (P = 0.005), and C (P < 0.001) and in Bufo americanus
numbers between treatment years at ponds A (P = 0.002), B (P < 0.001), and C
(P < 0.001). Differences between treatment years in most other cases were not
apparent due to low sample sizes.
|
Table 1.
Numbers of adult and neonatal individuals captured by species, pond and year.
(*
indicates ponds containing fish.) |
|
|
Pond A |
Pond B |
Pond C |
Pond D |
|
|
2001 |
2002 |
2001* |
2002 |
2001* |
2002 |
2001 |
2002 |
|
A. texanum
adults |
46 |
59 |
11 |
24 |
13 |
10 |
60 |
42 |
|
A. texanum
neonates |
17 |
5 |
0 |
10 |
0 |
94 |
0 |
1 |
|
R. sylvatica
adults |
10 |
15 |
7 |
5 |
1 |
4 |
24 |
46 |
|
R. sylvatica
neonates |
0 |
0 |
1 |
0 |
0 |
6 |
0 |
7 |
|
Rana catesbiana
neonates |
37 |
0 |
29 |
0 |
29 |
0 |
2 |
0 |
|
B. americanus
adults |
47 |
21 |
72 |
49 |
8 |
3 |
4 |
7 |
|
B. americanus
neonates |
103 |
116 |
160 |
813 |
0 |
17 |
3 |
0 |
 |
Figure 5.
Number of breeding season adults and emerging neonates. |
 |
Figure 6.
Reproductive success as a proportion of emerging neonates to breeding adults. |
 |
Figure 7.
Number of breeding season adults and emerging neonates. |
Conclusions
Prior to
removal, Ameiurus melas had a negative impact on Bufo reproduction. Prior to
removal, presence of centrarchid predators (Lepomis spp.) had
a negative impact on Ambystoma reproduction.
Bufo
americanus, Ambystoma texanum, and Rana sylvatica are capable of
successfully hatching and completing metamorphosis in ponds treated with
RotenoneTM. Amphibian
species may benefit from eradication of fish from breeding ponds by
pesticide application.
Acknowledgements
I would like to
thank the following individuals and institutions for their technical, financial,
and /or moral support and guidance during the course of this study:
Eastern Illinois University Biological Sciences Department: Dr.
Stephen J. Mullin, Dr. Robert U. Fisher, Dr. Kipp Kruse, and Dr. Scott
Meiners
Illinois Department of Natural Resources: Robert
Szafoni and Michael Mountz
Aubrey Leffel,
James Wachtel, Daphne Kampinga, Danial Cox
Erin Casey, C.
Drew Foster, Jennifer M. Fish and Rev. Paul Hampton. |