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Vernal Pools: Physical Characteristics and How
They Affect Breeding Success of Amphibians
Ben Klein
Description of Research
Previous studies have found vernal pools are critical for reproduction
in several amphibian species (Smith 1956, Shoop 1965, 1968). Vernal pools
are temporary bodies of water that form in spring after snowmelt and usually
dry in mid to late summer (Petranka 1998). Pools provide the necessary
habitat for these amphibian species to breed with little predation from
fish (De Graaf et. al. 1983). Many studies have found particular pool
characteristics important to breeding success, particularly temperature
and pH (Petranka 1998). Previous studies have estimated wood frog (Rana
sylvatica) and spotted salamander (Ambystoma maculatum) breeding success
to determine habitat quality. The purpose of my study was to document
the physical characteristics of vernal pools and estimate the breeding
success of these two species at the Huntington Wildlife Forest (HWF) in
the central Adirondacks, in upstate New York.
Wood frogs and spotted salamanders were chosen for this study because
of their relatively high abundance and their sensitivity to local disturbance
(Petranka 1998). The wood frog ran ges
from northern Georgia to treeline in Alaska, and breeds from March to
July at temperatures of approximately 10 degrees Celsius (Smith 1956).
The spotted salamander ranges from Nova Scotia through the eastern United
States and as far west as Kansas and Texas. Populations of spotted salamanders
have been declining in recent years (Petranka 1998). They are a nocturnal
species, and are generally considered fossorial (Petranka 1998). The breeding
season of the spotted salamander is from March to mid-April.
The objectives of this study were to 1) document the physical characteristics
of the pools at the Bureau Brothers Turn (BBT) study site, 2) quantify
breeding success of the vernal pools by counting wood frog and spotted
salamander egg masses and emergents, and 3) compare these results to other
vernal pools at HWF. I tested the null hypothesis that there would be
no difference in pool characteristic variables between BBT site pools
and pools at other sites at HWF.
This study was conducted at Huntington Wildlife Forest, a 15,000 acre
research area owned by the State University of New York College of Envrironmental
Science and Forestry. The two sites at HWF were quite similar in their
make-up. One site, the BBT site, was situated in the central portion of
the property, while the other sites were scattered throughout the southern
part of the property. Both sites were mixed northern hardwood forest,
and lay between the elevations of 550 and 650 meters.
Various physical characteristics and evidence of breeding were recorded
during sampling. Physical characteristics measured included: pool length,
width, depth, temperature, pH, substrate type (mud/silt, leaf litter,
or vegetation), and percent cover of emergent vegetation, cyanobacteria,
and tree canopy. To estimate breeding success, egg masses, tadpoles/larvae,
and emerging metamorphs were surveyed. Any other frog species, adult or
otherwise, seen in the pool was also recorded.
Pool depth (P=0.014), length (P<0.001), and width (P=0.044) were significantly
different at BBT pools compared to other HWF pools (Table
1). Average water depth for BBT pools was 14.1 cm (standard deviation=6.3),
compared to 38.8 cm (standard deviation =11.7) outside t he
BBT site. Average length for BBT pools was 6.40 m (standard deviation
=2.77), compared to 18.08 m (standard deviation =1.84) outside the BBT
site. Averagewidth for BBT pools was 3.51 m (standard deviation =1.62),
compared to 6.16 m (standard deviation =1.30). All other variables tested
were not significantly different (Table 1).
No breeding success was observed at the BBT site. No egg masses, tadpoles,
or metamorphs were observed during pool sampling. Additionally, breeding
behavior was not observed in adult frogs or salamanders found in the BBT
pools. Breeding success, however, was observed at the other pools at HWF
used in this study (Endriss 2001).
Physical characteristics of vernal pools appear to be strongly related
to the breeding success of spotted salamanders and wood frogs (Seale 1982,
Brodman 1995). Shoop (1974) found water depth important to breeding success.
Pools at BBT were shallower than a threshold suggested by Seale's (1982)
study for significant amphibian egg deposition. In my study, shallow pool
depth could be due to a lack of precipitation in HWF - April and May were
particularly dry at HWF in 2001. Average length and width of BBT pools
was also less compared to pools in Seale's study (1982). Conversely, the
other pools sampled at HWF, that successfully supported amphibian eggs,
tadpoles/larvae, and metamorphs, were consistent in depth, length, and
width with Seale's (1982) study pools. Therefore, my study suggests vernal
pool depth and size are important in determining breeding success in wood
frogs and spotted salamanders.
About The
Author: Ben Klein
I am currently an undergraduate at SUNY-ESF, majoring in Wildlife Science,
minoring in secondary education. Research interests include carnivore
ecology, and raptor ecology. Other interests are rock and ice climbing,
mountaineering, backpacking, and fly-fishing. After graduation, I plan
on attending graduate school out west and then hopefully working as a
wildlife biologist or wildlife interpreter in a National Park.
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