Dietary Selection Among Different Size Classes of Larval Ambystoma jeffersonianum (Jefferson Salamanders)
Jeff H. Bardwell, Christopher M. Ritzi, and James A. Parkhurst
Northeastern Naturalist, Volume 14, Issue 2 (2007): 293–299
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2007 NORTHEASTERN NATURALIST 14(2):293–299
Dietary Selection Among Different Size Classes of Larval
Ambystoma jeffersonianum (Jefferson Salamanders)
Jeff H. Bardwell*,1,2, Christopher M. Ritzi2, and James A. Parkhurst1
Abstract - This study examines changes in the frequency/abundance of prey selection
among five size classes of 183 Ambystoma jeffersonianum (Jefferson Salamanders)
within a natural, unmanipulated environment. Significant differences were found in
prey selection among size classes in vertebrate and macroinvertebrate (specifically
coleopteran and dipteran) prey groups, but not microinvertebrates. Predator-size
thresholds were noted as diet shifted from predominantly microinvertebrates to increasingly
larger macroinvertebrates to the final dietary selection of other vertebrates.
This study augments the catalogue of ingested Ambystoma prey and re-examines the
nature of ontogenous dietary selection.
Introduction
Among North American salamanders, aquatic Ambystoma larvae possess
several characteristics that make them ideal for studying trophic interactions:
first, Ambystoma grow to relatively large sizes and are common
throughout the continental United States; second, they have a high reproductive
fecundity; and third, larvae are isolated from adults for months within
their natal pools (Martof et al. 1980, Petranka 1998).
Larval Ambystoma diet selection has previously been studied within
natural and, with various degrees of manipulation, artificial environments.
Experiments using natural pools emulate realistic conditions of predator
populations, prey availability, and prey selection, but are limited in availability,
time, and replication (Benoy et al. 2002, Brophy 1980, Cortwright
1988, Smith and Petranka 1987). Artificial pools containing imported water
and detritus from natural areas allow increased replication and manipulation
of predator/prey ratios while maintaining a facsimile of natural conditions
(Morin et al. 1983, Walls and Williams 2001). Other studies have created
controlled lab environments where predators are presented with predetermined
quantities and types of prey (Leff and Bachmann 1988, Sih and
Petranka 1988). The two latter methods artificially manipulate predator/prey
population numbers, but allow for the examination of more precise questions
and increased statistical replications.
Ontogenous diet trends among salamanders have been well studied as
they relate to prey size: foraging larval salamanders, including Ambystoma
jeffersonianum (Green) (Jefferson Salamander), are limited by their mouth
1Department of Fisheries and Wildlife Sciences, Virginia Polytechnic Institute and
State University, Blacksburg, VA 24060. 2Current address - Department of Biology,
Sul Ross State University, Alpine, TX 79830. *Corresponding author -
urodela1@yahoo.com.
294 Northeastern Naturalist Vol. 14, No. 2
gape (Smith and Petranka 1987, Zaret 1980). Most ontogenous larval Ambystoma
studies have compared predator size and diet selection based on
prey size and species (Brophy 1980, Holomuzki and Collins 1987, Johnson
et al. 2003, Leff and Bachmann 1988, Smith and Petranka 1987). Studies
have also included other prey variables such as capture time, seasonal
variations, and electivity indices (Dodson 1970, Holomuzki and Collins
1987, Leff and Bachmann 1988).
The objectives of this project were to (1) examine the relative difference
of frequency and abundance of prey selected by larval Jefferson Salamanders
sampled within an unmanipulated, natural population via stomach
content analysis, and (2) quantify the trends and significant differences in
diet selection among size classes within the sample to observe the nature of
ontogenous selectivity.
Field Site Description
The study site chosen was an old, diked farm pond (approximately 0.2–
0.4 ha) within a small tongue of fragmented woodlands protruding from the
main tract of mesic hardwood forest located on Virginia Tech’s Kentland
Farm Research Facility in Montgomery County, VA (37º13'45"N,
-80º24'50"E). Jefferson Salamanders were the dominant predators, as the
pond did not contain bullfrogs, newts, turtles, or fish.
Methods
Salamander larvae were sampled during two collection trips within a
span of two weeks time in June/July 2004. Because prey resources within the
pond were observed in similar abundances for both sampling trials, the sum
total of samples per site within a single season were combined for analysis, a
method used in several prior studies involving larval Ambystoma diet
(Benoy et al. 2002, Brophy 1980, Dodson and Dodson 1971, McWilliams
and Bachmann 1989, Smith and Petranka 1987, Walls and Williams 2001).
The assumption that ambient prey abundances do not significantly change
between sampling periods has yet to be tested for Jefferson Salamanders.
Salamanders were captured primarily using a stationary seine aided by
herding. This technique was accomplished by stomping and splashing
through the water toward the net. Other methods (i.e., random sweeping
patterns, hand sampling, and aiming toward ripples) yielded inconsistent
harvests. Captured salamanders were euthanized in 70% ethanol and identified
using larval taxonomic keys (Altig and Ireland 1984).
Prey selection
A ventral sagittal incision was made in each specimen, and the stomach
extracted. Stomachs were placed into petri dishes, bisected, and flushed
using 70% ethanol. Contents were examined using a dissecting microscope
and identified to the lowest taxonomic level possible using field guides
(Conant and Collins 1998) and taxonomic keys (Thorp and Covich 2001).
2007 J.H. Bardwell, C.M. Ritzi, and J.A. Parkhurst 295
Each taxonomic category of stomach contents for each salamander was
quantified by frequency and abundance (Table 1). Prey cover classes, similar
to those first used by Nudds and Bowlby (1984) to analyze fish dietary
component abundances, were used for volumetric estimation of each
stomach’s prey contents. Eleven cover-class values were assigned using a
scaled percentage distribution to decrease visual estimation error. An estimated
range of zero contents would get a cover class of zero. An estimated
range of 0–2.5% proportional abundance of stomach contents received a
cover-class value of 0.0125; 2.5–10%, 0.0625; 10–21%, 0.155; 21–35%,
0.28; 35–50%, 0.425; 50–65%, 0.575; 65–79%, 0.72; 79–90%, 0.845; 90–
97.5%, 0.9375; and 97.5–100%, 0.9875.
Dietary significance
The predator-population sample consisted of a total length (TL) size
range of 3.0–7.5 cm and was subdivided into five size classes (SC), each
spanning 0.5 cm, except SC 1 and SC 5. The nature of stomach-content
data measurements (Magnusson et al. 2003) lends itself to skewed and
bimodal distributions. Therefore, cover-class volumetric estimations
(each data point was limited to one of eleven possible cover classes) were
left untransformed for statistical analysis (Table 2). A Kruskal-Wallis test
was performed using SPSS ver. 11.5, using a Nemenyi post hoc test on
significant factors (Zar 1999).
Results
Prey selection
Diet selection analysis for Jefferson Salamanders was based on the
proportional differences of each prey category within the stomach contents
of the entire sample (n = 183), independent of the predator’s size. To achieve
Table 1. Ambystoma jeffersonianum (Jefferson Salamander) diet frequency and mean abundance;
L = larval prey, A = adult prey, * = new dietary record for A. jeffersonianum.
Prey category Frequency Mean abundance
Microinvertebrates (Nematoda) 172 0.94
Macroinvertebrates 161 0.16
Coleoptera L/A 11 0.28
Diptera L 106 0.06
Hemiptera/Homoptera L/A 7 0.43
Odonata L 2 0.28
Orthoptera A 1 0.43
Megaloptera L 3 0.01
Lepidoptera* L 1 0.56
Unidentified insects 16 0.06
Vertebrates 2 0.85
Rana sylvatica A 1 0.85
Ambystoma jeffersonianum L 1 0.94
Empty 11 -
Total (n) 183
296 Northeastern Naturalist Vol. 14, No. 2
greater resolution, large-prey categories were split into more basal taxonomic
groups. Microinvertebrates were not split into subgroups, but identified
as Nematoda and/or unidentifiable unicellular green algae in binucleate
paired clumps. Other zooplankton beyond nematodes were not observed
within the stomach contents. Macroinvertebrates were identified to order:
Coleoptera, Diptera, Hemiptera, Lepidoptera, Megaloptera, Odonata, Orthoptera,
and unidentified. Vertebrates were identified to species: Jefferson
Salamander and Rana sylvatica (LeConte) (Wood Frog). All stomachs that
contained food were distended similarly and contained various amounts of
microinvertebrates inversely proportional to the amount of macro-invertebrate
or vertebrate prey ingested.
Dietary significance
The five size classes of larvae were divided as follows: SC 1: 3.0–4.5 cm
(n = 21); SC 2: 4.5–5.0 cm (n = 25); SC 3: 5.0–5.5 cm (n = 46); SC 4: 5.5–6.0
cm (n = 65); and SC 5: 6.0–7.5 cm (n = 26). Only two main prey groups
exhibited significantly different abundances among size classes ( = 0.05):
macroinvertebrates (0.022) (coleopterans [0.047] and dipterans [0.041]) and
vertebrates (0.016). Several groups expressed trends toward significant
abundance differences among size classes ( = 0.1), including
microinvertebrates (0.084) and unidentified insects (0.058). All other prey
groups lacked significant differences among size classes (Table 2).
Discussion
Prey selection
This study lends further support to the finding that microinvertebrates
(daphnia, copepods, ostracods, or nematodes) appear consistently in larval
Ambystoma diets (Brophy 1980, Freda 1983, Wilson and Meret 2003,
Table 2. Results of a Kruskal-Wallis test with Nemenyi post hoc analysis ( = 0.05) to
determine the degree of selection between size classes per prey category: results denoted by
insignificant groups (i.e., 1–3), insignificant groups with zero abundance values (underlined:
i.e., 1–3) and significant differences between groups (i.e., 1 < 2–3–4–5)
Prey category 2 df P-value Size class selection
Microinvertebrates (Nematoda) 8.204 4 0.084
Macroinvertebrates 11.476 4 0.022 1 < 2–3–4–5
Coleoptera 9.637 4 0.047 1–3 < 2 < 4–5
Diptera 9.996 4 0.041 1–2–4–5 < 3
Hemiptera/Homoptera 4.706 4 0.319
Odonata 5.989 4 0.200
Orthoptera 1.815 4 0.770
Megaloptera 3.229 4 0.520
Lepidoptera 6.320 4 0.176
Unidentified insects 9.144 4 0.058
Vertebrates 12.143 4 0.016 1–2–3–4 < 5
Ambystoma jeffersonianum 6.038 4 0.196
Rana sylvatica 6.038 4 0.196
2007 J.H. Bardwell, C.M. Ritzi, and J.A. Parkhurst 297
Wurst and Mull 1999), as reflected by the high frequency and mean abundance
data we observed (Table 1). Excluding the dipterans (specifically
chironomids and chaoborids), most aquatic insects usually are recorded at
low frequencies and abundances or not at all (Brophy 1980, Dodson and
Dodson 1971, Smith and Petranka 1987). This is consistent with the low
frequencies and mean abundances historically recorded for most
macroinvertebrates and, by contrast, the high frequency and low mean
abundance of dipterans. This indicates that, although Jefferson Salamanders
may eat a large number of macroinvertebrates, the small size of
most prevents all but the largest orders from comprising a substantial mean
volumetric abundance within the salamanders’ diet (Table 1). Aquatic
amphibians also occurred in low frequency, as previously indicated in the
literature (Dodson and Dodson 1971, Freda 1983). However, when consumed,
a substantial proportion of the diet was comprised of a single
vertebrate prey item. Although larval Jefferson Salamanders did not eat
vertebrates often, when they did so, the dietary reward to that individual
was significant.
Dietary significance
Although microinvertebrates did not vary statistically among size
classes, a trend toward reduced consumption with increasing predator
size was suggested. This trend is supported by documented decreases in
Daphnia (Leff and Bachmann 1988), ostracod, and copepod (Brophy
1980) consumption as larval Ambystoma size increased. SC 1 (3.0–4.5
cm) predominantly ate microinvertebrates. Macroinvertebrate consumption
rose significantly from SC 1 (3.0–4.5 cm) to SC 2 (4.5–5.0 cm),
suggesting that 4.5 cm may be a threshold for general macroinvertebrate
consumption. Utilization of two macroinvertebrate orders (coleopterans
and dipterans) increased significantly from SC 2 (4.5–5.0 cm) to SC 4
(5.5–6.0 cm) and SC 3 (5.0–5.5 cm), respectively, whereas the remaining
macroinvertebrate orders did not differ among size classes. Holomuzki
and Collins (1987) saw consumption of dipterans in “small” Ambystoma
expand to include five orders (Odonata, Ephemeroptera, Trichoptera,
Hemiptera, and Coleoptera) as they grew larger, three of which were
present in SC 2–5 (4.5–7.5 cm). Finally, vertebrate, including conspecifics,
consumption did not occur until SC 5 (6.0–7.5 cm). Vertebrate consumption
is rare in larval Ambystoma diet studies and, if it occurs at all,
is limited to one or two occurrences per hundreds of specimens
(Holomuzki and Collins 1987, Smith and Petranka 1987). Vertebrate consumption
appears limited by the size, morphology, and, possibly, the
seasonal collection times of the Ambystoma samples. Exceptions to these
trends involve cannabalistic A. tigrinum (Green) (Tiger Salamander) and
A. mavortium Baird (Western Tiger Salamander) morphs (Smith and
Petranka1987, Wurst and Mull 1999).
The ecological significance of dietary ontogenous shifts extends beyond
a catalogue of Jefferson Salamander diet. These salamanders, as top
298 Northeastern Naturalist Vol. 14, No. 2
predators within their aquatic lotic habitats, mold the entire trophic dynamic
of these isolated pool communities as they grow. To varying extents,
the survival success of phytoplankton and planktonic diptera may be
manipulated by the “smallest” Jefferson Salamander, the synchronized
seasonal breeding of zooplankton and lotic invertebrates by the “medium”
sized Jefferson Salamander, and vertebrate larvae mortality by the “largest”
Jefferson Salamander, whose mouth gapes have grown wide enough
for such prey.
Acknowledgments
First and foremost, we thank our volunteer field crew—Kelly Berger, Ransom
Hughes, and Joshua Evans—for slogging through knee-deep mud and submerged
snags. Thanks to Chris d’Orgeix, Don Mackler, and Mike Pinder for their valuable
assistance in site location, sample identification, and permit acquisition, respectively.
Finally, we thank Dr. Carola Haas for helpful consultation during this
project’s early stages. Specimens were collected under Virginia Department of Game
and Inland Fisheries Permit no. 024026. This project was reviewed and approved
(#04-011-F&W) by Virginia Tech’s Animal Care Committee.
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