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2003
Accelerated Hatching of Southern Leopard Frog (Rana
sphenocephala) Eggs in Response to the Presence of a Crayfish
(Procambarus nigrocinctus) Predator
Daniel Saenz
Wildlife Habitat and Silviculture Laboratory, Southern Research Station, U.S.D.A. Forest Service,
Nacogdoches, TX 75962
James B. Johnson
Stephen F Austin State University
Cory K. Adams
Stephen F Austin State University
Gage H. Dayton
Texas A & M University - College Station
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Repository Citation
Saenz, Daniel; Johnson, James B.; Adams, Cory K.; and Dayton, Gage H., "Accelerated Hatching of
Southern Leopard Frog (Rana sphenocephala) Eggs in Response to the Presence of a Crayfish
(Procambarus nigrocinctus) Predator" (2003). Faculty Publications. 146.
https://scholarworks.sfasu.edu/biology/146
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Copeia, 2003(3), pp. 646–649
Accelerated Hatching of Southern Leopard Frog (Rana sphenocephala)
Eggs in Response to the Presence of a Crayfish
(Procambarus nigrocinctus) Predator
DANIEL SAENZ, JAMES B. JOHNSON, CORY K. ADAMS,
AND
GAGE H. DAYTON
Phenotypic plasticity, such as morphological and behavioral changes in response
to predators, is common in larval anurans. Less is known about inducible defenses
in the embryonic stages of development. We investigated the predation risk imposed
by crayfish (Procambarus nigrocinctus) on southern leopard frog (Rana sphenocephala)
eggs and whether crayfish presence induces a change in the timing of hatching of
R. sphenocephala eggs. We found that crayfish significantly reduce the hatching success of R. sphenocephala eggs by eating them and that eggs hatch significantly faster
in the presence of crayfish than when crayfish are not present. We also found that
the nonlethal presence of crayfish (caged with no access to eggs) induced accelerated hatching, indicating that injured conspecifics are not required to elicit the response. Reception of chemical cues produced or released by crayfish may play an
important role in survival of R. sphenocephala eggs.
A
NURAN larvae are known to alter their behavior (Skelly, 1994; Wilbur, 1997; Van
Buskirk, 2001) and change their shape and color (McCollum and Leimberger, 1997; Van Buskirk et al., 1997) to increase survival in the presence of an array of predators. These plastic behavioral and developmental antipredator responses by amphibian larvae appear to be
common coping mechanisms (Relyea, 2001).
Less is known about induced antipredator defenses of the embryonic stages of amphibians.
Changes in the timing of the transition between
egg and larval stages in the presence of predators have been documented for several species
of anurans. Sih and Moore (1993) were the first
to demonstrate that predation risks may affect
the timing of hatching. They showed that salamander (Ambystoma barbouri) eggs, laid aquatically, delayed their hatching to a later time in
the presence of a larval predator, the flatworm
(Phagocotus gracilis), and in the presence of water-borne flatworm chemical cues. Later, Moore
et al. (1996) found that A. barbouri eggs also delayed hatching in response to chemical cues
from a predatory fish (Lepomis cyanellus).
Many more studies have documented an accelerated hatching response to a variety of egg
predators. Warkentin (1995, 2000) showed that
vibratory cues from the oophagous snake (Leptodeira septentrionalis) and the wasp (Polybia rejecta) would cause early hatching of well-developed red-eyed treefrog (Agalychnis callidryas)
eggs. Similarly, Brown and Iskandar (2000)
found that well-developed Rana arathooni embryos would hatch prematurely when physically
agitated by human collectors. Both A. callidryas
and R. arathooni lay their eggs terrestrially near
water.
Agalychnis callidryas also hatch early in response to contact with hyphae of the pathogenic fungus (Pheaosphaeriaceae: Dothideales),
possibly stimulated by oxygen depletion caused
by the fungus, chemical cues released by the
fungus, or cues from clutchmates that die as a
result of fungal infection (Warkentin 2001).
Chivers et al. (2001) found that water-borne
chemical cues from egg-eating leeches accelerated hatching in the Pacific treefrog (Hyla regilla) and the Cascade frog (Rana cascadae).
Because eggs are immobile, they would appear to be the most vulnerable stage in a frog’s
development. Eggs are preyed on by conspecific
anuran larvae (Polis, 1981; Petranka and Kennedy, 1999; Dayton and Wapo, 2002), other species of anuran larvae (Crossland, 1998), invertebrate predators (Warkentin, 1995; Richter,
2000; Chivers et al., 2001), and fish (Grubb,
1972). However, some anuran eggs are unpalatable or even toxic to some potential predators
(Licht, 1968; Punzo and Lindstrom, 2001).
Southern leopard frog (Rana sphenocephala)
eggs may be particularly apparent to predators
because they are deposited as large conspicuous
masses, often as aggregated clumps (Caldwell,
1986) ranging from several hundred to a few
thousand per clump. The rate of egg development varies, and eggs can take more than 10
days to hatch when water temperature is low
(DS, pers. obs.), thus affording predators ample
time to find the eggs. Richter (2000) observed
caddisflies (Trichoptera) predating R. sphenocephala egg masses in Mississippi and suggested
q 2003 by the American Society of Ichthyologists and Herpetologists
SAENZ ET AL.—HATCHING RESPONSE IN RANA SPHENOCEPHALA
that the aggregation of egg masses may facilitate
movement of predators between clumps of
eggs. In this paper, we examine the effect of the
crayfish (Procambarus nigrocinctus), a common
scavenger/predator on the timing and success
of hatching of R. sphenocephala eggs. We chose
P. nigrocinctus because it is widespread throughout our study region and commonly coinhabits
pools with R. sphenocephala (DS, pers. obs.).
MATERIALS
AND
METHODS
We collected 30 crayfish, between 60 and 70
mm total length, from the Davy Crockett National Forest in eastern Texas during November
and December 2001. Prior to the experiments,
crayfish were housed in 3-liter tubs (19 3 9 3
33.5 cm) with aged tap water. They were each
fed approximately 0.5 g of tropical fish food every three days prior to the experiments. No attempt was made to control for sex or molt status. We also collected 15 R. sphenocephala egg
masses in varying stages of development (between stages 5–10; Gosner, 1960) from the Stephen F. Austin Experimental Forest in Nacogdoches County in eastern Texas on 21 December 2001.
Our experimental design consisted of three
treatments: (1) a control group with 25 R. sphenocephala eggs; (2) a group with 25 R. sphenocephala eggs and a free roaming crayfish with access to eggs; and (3) a treatment containing 25
R. sphenocephala eggs and a caged (cage dimensions: 14 3 9 3 14 cm) crayfish that did not
have access to the eggs. In the latter treatment,
water flowed freely between the crayfish and the
eggs. Caged crayfish were not fed during the
experiment. Each treatment was replicated 15
times using a subset of eggs from each clutch.
Each replicate was placed into a 3-liter plastic
tub (19 3 9 3 33.5 cm) with two-liters of aged
tap water. Temperature in the laboratory varied
between approximately 10 and 13 C where the
experiments were conducted.
To determine hatching success, we observed
the tubs every 24 h until all normally developed
embryos had hatched, at which time the experiment was terminated. Any remaining eggs that
showed no signs of development were assumed
to be incapable of hatching. Crayfish were removed from the tubs, and counts were made of
newly hatched tadpoles and of eggs that failed
to hatch. Crayfish in the free-roaming treatment
were capable of eating eggs and hatchlings,
which may have influenced our measure of
hatching success. Proportional data (percent
eggs that hatched) were arcsine-square-root
transformed and used in an analysis of variance
647
(ANOVA) followed by Tukey’s multiple comparison test to compare egg survival between treatments.
To assess hatching timing, we observed the
tubs every 24 h until we noted hatchlings from
any tub in any treatment within a replicate (full
siblings), thus indicating that the egg mass was
beginning to hatch. For each egg mass, the
number of hatchlings present in each tub was
counted 24 h after hatching began in any treatment. The proportion hatched was calculated as
a fraction of viable eggs only; nonviable eggs
were excluded from the analysis. In the freeroaming crayfish treatment, where the crayfish
ate eggs, we calculated hatching rate from the
remaining live eggs. This method was repeated
for each replicate until all 15 egg masses had
hatched. The earliest clutch hatched completely
in four days, whereas the slowest took eight days
to hatch from the time they were collected in
the field. Proportional data (percent eggs
hatched by 24 h) were arcsine-square-root transformed and used in an analysis of variance (ANOVA, randomized block design) followed by
Dunnett’s multiple comparison test to compare
the hatching rate of the two treatments to the
control. A paired t-test was used to compare the
effect of the two predator treatments on the
hatching rate. Statistical analyses were performed using SPSS version 10.0 (SPSS Inc.,
1999, Chicago, IL).
RESULTS
Hatching success differed significantly among
the three treatments (ANOVA F2,42 5 43.28, P
, 0.001). Tukey’s post hoc tests (Critical Value
of Studentized Test 5 3.45) revealed that tubs
with free-roaming crayfish had a significantly
lower hatching success (42 6 10%, mean 1 SE)
compared to control tubs (97 6 2%) and tubs
with caged crayfish (98 6 1%). In every case (n
5 15), the free-roaming crayfish consumed at
least a portion of the 25-egg clump, but only
three crayfish consumed all 25 eggs. The egg
predation that occurred in tubs containing freeroaming crayfish was likely the primary cause of
hatching failure in the experiment. However,
crayfish also were capable of eating hatchlings,
which might have caused an overestimation of
crayfish predation on eggs. Hatching success in
the majority of control tubs and caged crayfish
tubs was less than 100%. The main cause of
hatching failure appears to be unfertilized eggs,
since there were no signs of development in the
unhatched eggs. We found no difference in
hatching success between control and caged
crayfish treatments.
648
COPEIA, 2003, NO. 3
The timing of hatching also differed among
the three treatments (ANOVA F2,39 5 6.55, P 5
0.005). The proportion of eggs hatched in 24 h
after the start of hatching was significantly lower
in the control tubs (41 6 10%) than in either
the caged crayfish tubs (58 6 7%) or the freeroaming crayfish tubs (70 6 8%; critical value
of Dunnett’s t 5 2.01). We found no difference
in the timing of hatching between caged crayfish and free-roaming crayfish treatments
(paired t-test: t 5210.32, df 5 11, P 5 0.21). It
is possible that the free-roaming crayfish ate
hatchlings, thereby skewing our results toward
a more conservative estimate of the acceleration
of hatching than actually occurred. In three instances, free-roaming crayfish ate all 25 eggs before the second day of hatching.
DISCUSSION
Our study suggests that crayfish (P. nigrocinctus) can significantly affect survival of R. sphenocephala eggs. Crayfish consumed slightly over
half of the eggs in the free-roaming crayfish
treatment. Predatory crayfish were observed
pulling embryos from the egg capsules. The embryos were then consumed and the egg capsules
discarded. Differences in the timing of hatching
observed in our study clearly indicate that R.
sphenocephala eggs respond to the presence of a
crayfish by reducing the time to hatching. Similar responses are known from other anurans.
Warkentin (1995, 2000, 2001) showed that an
effective defense strategy to prevent mortality
on red-eyed treefrog eggs is to hatch more
quickly in the presence of predators and pathogens. This species typically lays its eggs on vegetation overhanging water. As the eggs hatch,
tadpoles fall into the water where they are safe
from terrestrial egg predators. Warkentin
(1995) also demonstrated that the trade-off of
early hatching leads to greater susceptibility of
underdeveloped tadpoles to aquatic predators.
More research is needed to ascertain potential
costs of early hatching in R. sphenocephala.
Prior to this research, H. regilla and R. cascadae were the only anurans that were known to
accelerate the timing of hatching in response to
aquatic egg predators (Chivers et al., 2001). We
present the first evidence of early hatching of
R. sphenocephala eggs in response to a predator.
We suggest that crayfish would likely have less
success in predating a free-swimming tadpole
than sessile eggs despite the protection afforded
by the egg capsules or any toxins that R. sphenocephala eggs may contain. We noted that hatchling R. sphenocephala are generally inactive but
are capable of swimming when disturbed as
soon as they leave the egg capsule, which should
enable them to disperse and hide in the substrate.
Proximate mechanisms of how R. sphenocephala embryos detect the presence of predators are
unknown. Other studies have identified tactile
stimulation or agitation as mechanisms for inducing an early hatching in fish (Griem and
Martin, 2000) as well as anuran eggs (Warkentin, 1995, 2000; Brown and Iskandar, 2000). In
our free-roaming treatment, crayfish were able
to physically disturb eggs. Thus, tactile stimulation may have played a role in early hatching
for this treatment. Free-roaming crayfish also
consumed some of the eggs in each tub, which
may have resulted in a chemical alarm stimulus
that led to accelerated hatching in the other
embryos. Alarm pheromones that alert conspecifics of danger are known to accelerate hatching in H. regilla (Chivers et al., 2001) and are
released by several species of anuran tadpoles
when attacked by predators (Petranka, 1989).
However, direct mechanical stimulation and
alarm pheromones cannot explain the accelerated hatching response we observed in the
caged crayfish treatment. It appears that the
mere presence of a crayfish can induce early
hatching in R. sphenocephala since caged crayfish
were not fed during the experiment and were
not allowed to come in direct contact with the
eggs. Most likely, crayfish release cues into the
water that are detected by the eggs via chemoreception. Future research is needed to determine the causal mechanisms underlying the accelerated hatching phenomenon we observed.
ACKNOWLEDGMENTS
We thank N. E. Koerth for advise with the
analyses for this study and R. N. Conner, R. B.
Langerhans, G. Perotti, and three anonymous
reviewers for comments on an earlier draft of
this manuscript. Rana sphenocephala eggs were
collected under Texas Parks and Wildlife Department Scientific Permit SPR-0490-059. All appropriate animal care guidelines were followed
(see guidelines for use of live amphibians and
reptiles in field research, American Society of
Ichthyologists and Herpetologists).
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(DS) WILDLIFE HABITAT AND SILVICULTURE LABORATORY, SOUTHERN RESEARCH S TATION ,
USDA FOREST SERVICE, NACOGDOCHES, TEXAS
75965; ( JBJ, CKA) DEPARTMENT OF BIOLOGY,
STEPHEN F. AUSTIN STATE UNIVERSITY, NACOGDOCHES, TEXAS 75962; AND (GHD) DEPARTMENT OF WILDLIFE AND FISHERIES SCIENCES,
TEXAS A&M UNIVERSITY, COLLEGE STATION,
TEXAS 77843. E-mail: (DS) cpsaenzd@titan.
sfasu.edu. Send reprint requests to DS. Submitted: 23 Aug. 2002. Accepted: 8 March
2003. Section editor: M. E. Douglas.