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Evidence of a new niche for a North American salamander: Aneides vagrans residing in the canopy of old-growth redwood forest

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Abstract

Abstract.—We investigated habitat use and movements of the wandering salamander, Aneides vagrans, in an old-growth forestcanopy. We conducted a mark-recapture study of salamanders in the crowns of five large redwoods (Sequoia sempervirens) inPrairie Creek Redwoods State Park, California. This represented a first attempt to document the residency and behavior ofA. vagrans in a canopy environment. We placed litter bags on 65 fern (Polypodium scouleri) mats, covering 10% of their totalsurface area in each tree. Also, we set cover boards on one fern mat in each of two trees. We checked cover objects 2–4 timesper month during fall and winter seasons. We marked 40 individuals with elastomer tags and recaptured 13. Only onerecaptured salamander moved (vertically 7 m) from its original point of capture. We compared habitats associated withsalamander captures using correlation analysis and stepwise regression. At the tree-level, the best predictor of salamanderabundance was water storage by fern mats. At the fern mat-level, the presence of cover boards accounted for 85% of thevariability observed in captures. Population estimates indicated that individual trees had up to 29 salamanders. Large fernmats have high water-holding capacities, which likely enable year-round occupation of the canopy by A. vagrans. Otherobservations indicate that A. vagrans and its close relative A. ferreus also occupy additional habitats in forest canopies,especially moist cavities inside decaying wood.
Herpetological Conservation and Biology 1(1):16-26
Submitted: June 15, 2006; Accepted: July 19, 2006
16
INTRODUCTION
The temperate salamanders of North America are primarily
terrestrial and fossorial, except some species in the family
Plethodontidae that have been reported to occupy moist vertical
rock faces (genus Desmognathus) and several species (genus
Aneides) that climb into trees at least seasonally (Petranka 1998;
Waldron and Humphries 2005). However, there has been no
conclusive evidence of a temperate zone salamander species
completing its entire life cycle in an arboreal environment. This
report documents the year-round residency of the wandering
salamander, Aneides vagrans, in the canopy of old-growth
redwood forest in northwestern California.
Recent genetic evidence (Jackman 1998) indicated that the
clouded salamander (Aneides ferreus) consisted of two separate
species. A new species, the wandering salamander (A. vagrans),
was proposed for populations south of the south fork of the
Smith River in northwestern California. This species occurs
primarily in northern California with disjunct populations that
were introduced to Vancouver Island, British Columbia where
they are abundant in terrestrial habitats (Jackman 1998; Davis
2002b). The name A. ferreus was retained for populations that
occur primarily in western Oregon.
Aneides vagrans has a prehensile tail that it uses to assist in
climbing vertical surfaces (Petranka 1998; Spickler and Sillett,
pers. obs.) and long limbs with slender digits bearing sub-
terminal toe pads (Petranka 1998). This species has previously
been described as a primarily terrestrial salamander that is also
found on logs, in trees, and on shrubs. It occupies moist
terrestrial habitats, especially under exfoliating bark and in
cracks and cavities of decomposing logs, stumps, snags, and
talus (Davis 2002a; Stebbins 2003). Similarly, A. ferreus has
climbing ability with individuals found as high as 6.5 m in trees
and, in the laboratory, will leap from the hand to nearby objects,
clinging with great tenacity, even to vertical surfaces (Nussbaum et al.
1983). The arboreal salamander (A. lugubris) has been found in trees
over 18 m above ground, and may deposit eggs in decay holes in live
oak trees up to 9 m above ground (Staub and Wake 2005).
The first evidence that A. vagrans might reside in the temperate forest
canopies of the redwood region was the discovery of a clutch of eggs
(later hatched in the lab) inside a leatherleaf fern (Polypodium scouleri
Hook. & Grev.) mat that had been dislodged from high in the crown of
a redwood being felled for lumber (Welsh and Wilson 1995). Soon
after the first in situ scientific investigations of old-growth redwood
forest canopies began in 1996, we observed the arboreal presence of A.
vagrans (Sillett 1999). All observations were made of individuals and
pairs occupying tunnels and cavities in large epiphytic fern mats in
trees, except one observation (SCS) of a mummified adult found in a
shallow trunk cavity located 88 m above the ground in a large redwood
tree.
Our objective was to study A. vagrans inhabiting an old-growth
forest canopy in Prairie Creek Redwoods State Park, Humboldt County,
California, including several trees whose crowns have been explored by
two of us (JCS & SCS) since 1996. In particular, we investigated
habitat use, activity patterns, and movements in the crowns of five large
redwood trees to glean new information on the ecology of A. vagrans in
trees.
The Redwood Forest Canopy Environment.—Old-growth forests
dominated by Sequoia sempervirens (D. Don) Endl. (hereafter
‘redwood’) are home to some of the world’s tallest and largest trees.
Individuals can exceed 112 m in height, 7 m in diameter, and have
wood volumes over 1,000 m3 (Sawyer et al. 2000). Old-growth
redwood forests contain some of the oldest and most structurally
complex trees on the planet. These trees often live over 1000 years and
develop highly individualized crowns shaped by natural forces
EVIDENCE OF A NEW NICHE FOR A NORTH AMERICAN SALAMANDER:
ANEIDES VAGRANS RESIDING IN THE CANOPY OF OLD-GROWTH
REDWOOD FOREST
JAMES C. SPICKLER1, STEPHEN C. SILLETT1, SHARYN B. MARKS1,
AND HARTWELL H. WELSH, JR.2,3
1Department of Biological Sciences, Humboldt State University, Arcata, CA 95521, USA
2Redwood Sciences Laboratory, USDA Forest Service, 1700 Bayview Drive, Arcata, CA 95521, USA
3Corresponding Author, email: hwelsh@fs.fed.us
Abstract.—We investigated habitat use and movements of the wandering salamander, Aneides vagrans, in an old-growth forest
canopy. We conducted a mark-recapture study of salamanders in the crowns of five large redwoods (Sequoia sempervirens) in
Prairie Creek Redwoods State Park, California. This represented a first attempt to document the residency and behavior of A.
vagrans in a canopy environment. We placed litter bags on 65 fern (Polypodium scouleri) mats, covering 10% of their total
surface area in each tree. Also, we set cover boards on one fern mat in each of two trees. We checked cover objects 2–4 times per
month during fall and winter seasons. We marked 40 individuals with elastomer tags and recaptured 13. Only one recaptured
salamander moved (vertically 7 m) from its original point of capture. We compared habitats associated with salamander
captures using correlation analysis and stepwise regression. At the tree-level, the best predictor of salamander abundance was
water storage by fern mats. At the fern mat-level, the presence of cover boards accounted for 85% of the variability observed in
captures. Population estimates indicated that individual trees had up to 29 salamanders. Large fern mats have high water-
holding capacities, which likely enable year-round occupation of the canopy by A. vagrans. Other observations indicate that A.
vagrans and its close relative A. ferreus also occupy additional habitats in forest canopies, especially moist cavities inside decaying
wood.
Key Words.—Aneides vagrans, A. ferreus, Sequoia sempervirens, forest canopy, arboreal habitat use, salamander
Herpetological Conservation and Biology 1(1):16-26
17
(Van Pelt 2001). Disturbances (e.g., windfall, crown fires) that
increase light availability within tree crowns stimulate new
growth from damaged trunks and branches. In redwood, this
new growth can be in the form of either horizontal branches or
vertical trunks (hereafter reiterated trunks), each with its own set
of branches (Sillett 1999). Reiterated trunks can originate from
other trunks or from branches. When a trunk arises from a
branch, the branch thickens in response to the added weight and
hydraulic demand of the trunk, creating a “limb.” Trunks,
limbs, and branches also become fused with each other during
crown development (Sillett and Van Pelt 2001). The highly
individualized crowns of complex redwoods offer a myriad of
substrates and habitats for epiphytic plants and other arboreal
organisms (Williams 2006).
Crown-level complexity in redwoods promotes accumulation
of organic material, including epiphytic plants, on tree surfaces
(Sillett and Bailey 2003). Crotches between the trunks, the
upper surfaces of limbs and branches, and the tops of snapped
trunks provide platforms for debris accumulation. Vertical and
horizontal sections of dead wood also provide substrates for
fungal decomposition. Over time, this debris develops into soil
as organic materials decompose into humus, which provides a
rooting medium for vascular plants. The most abundant
vascular epiphyte in redwood rain forests is the evergreen fern,
P. scouleri (Sillett 1999), with individual trees supporting up to
742 kg dry mass of these ferns and their associated soils
(hereafter ‘fern mats,’ Sillett and Bailey 2003). As fern mats
grow in size and number, their effects on within-crown
microclimates become pronounced. Like a sponge, large fern
mats store water within the crown, increasing the humidity
(Ambrose 2004) and providing refuge for desiccation-sensitive
species, including mollusks, earthworms, and a wide variety of
arthropods (Sillett 1999; Jones 2005). Large fern mats also tend to be
internally complex, with tunnels and cavities between the rhizomes and
dense roots as well as interstitial space around embedded sticks
(Stephen Sillett, pers. obs.).
MATERIALS AND METHODS
Study Area.—We studied A. vagrans in five redwood trees located in
Prairie Creek Redwoods State Park (PCRSP), Humboldt County,
California within an old-growth redwood forest. Mean annual rainfall
in the study area was 1.67 m, with summer temperatures ranging from
7°–31° C and winter temperatures ranging from 1°–23°C during 2002–
2004. Trees were selected from a 1-ha permanent reference stand that
is 50 m elevation and 7 km from the Pacific Ocean. Within the
reference stand, redwood accounts for 95.8% of the trunk basal area
with the remainder consisting of Douglas-fir (Pseudotsuga menziesii
[Mirb.] Franco), hemlock (Tsuga heterophylla [Raf.] Sarg.), and a few
hardwoods.
We selected study trees (Fig. 1) on the basis of size, structural
complexity, and epiphyte abundance. Trees 1 (‘Kronos’) and 2 (‘Rhea’)
have interdigitating sections of their crowns, where fern-covered
branches and limbs allow the possibility of salamander movement from
tree-to-tree without going to the ground. Tree 3 (‘Demeter’) stands 16
m from Kronos and Rhea. Its crown does not interact with these trees,
so movement of a salamander between them would require ground
contact. Trees 4 (‘Prometheus’) and 5 (‘Iluvatar’) stand over 50 m from
each other and the other trees; they were selected because of their high
crown-level structural complexity and epiphyte loads.
Tree access.We achieved access to tree crowns by using a high-
powered compound bow mounted to an open-face fishing reel. A
rubber-tipped arrow trailing fishing filament was shot over branches
FIGURE 1. A two-dimensional display (view angle = 120°) of the three-dimensional crown structure of five redwood trees surveyed in this study. Main
trunks and reiterated trunks are shaded gray. Limbs are indicated by thin, black lines. No branches are shown. Locations of Polypodium scouleri fern
mats and Aneides vagrans captures are shown according to the legend. Note that “floating” symbols indicate locations on branches. “Sampled mats” are
fern mats that were selected for placement of cover objects.
Spickler et al.—Aneides vagrans in Redwood Canopies September 2006
18
high in the crown, and a nylon cord was then reeled back over
the branches and used to haul a 10 mm diameter static
kernmantle climbing rope into the crown and back to the
ground. One end of the climbing rope was then anchored at
ground level, and the other end was climbed via single rope
technique (Moffett and Lowman 1995). We had access to the
rest of the crown via arborist-style rope techniques (Jepson
2000; Fig. 2). The climbing rope was threaded through a pulley
hung from a sturdy branch near the treetop. The rope could be
easily replaced with nylon cord when the tree was not being
climbed.
Tree crown mapping.—We described tree crowns by
measuring dimensions of the main trunk and all reiterated trunks
with a basal diameter over 5 cm. We measured trunk diameters
at 5 m height intervals. For reiterations arising from the main
trunk or other reiterated trunks, we recorded: top height, base
height, basal diameter, and distance and azimuth (i.e., compass
direction) of base and top from center of main trunk. For
reiterations arising from limbs we recorded the following
additional measurements: limb basal diameter, diameter of limb
at the base of the reiteration, and limb height of origin. Thus, the
XYZ coordinates and architectural context of every measured
diameter could be determined for use in 3-dimensional mapping.
Total tree height was determined by dropping a tape from the
uppermost foliage to average ground level.
We derived three structural variables and three fern mat variables
from the mapping data, including total fern mat mass (kg), fern mat
mass in crotches, proportion of fern mass in crotches, main trunk
volume (m3), reiterated trunk volume, and limb volume. Volumes of
main trunks, reiterated trunks, and limbs were estimated by applying the
equation for a regular conical frustum to the diameter data (Table 1)
such as:
Volume = Length × π/3 × (lower radius2 + lower radius × upper radius
+ upper radius2).
In each tree, we also determined the XYZ coordinates of all P. scouleri
fern mats by measuring their heights above ground as well as their
distances and azimuths from the main trunk. Fern mat size was
quantified by the following measurements: mat length, mat width,
average soil depth (calculated from multiple measurements with a metal
probe), and maximum frond length. We calculated surface areas of fern
mats by applying the equation for an ellipse:
Area = π × 0.5(mat length) × 0.5(mat width).
Surface area was multiplied by average soil depth to calculate fern
mat volume. Dry masses of all mats were estimated by applying the
following model equation (n = 18, R2 = 0.995; unpubl. data of Sillett
FIGURE 2. Left, a climber (Steve Sillett) ascends a large redwood in Prairie Creek Redwoods State Park, California, in search of Aneides vagrans.
(Photograph by Marie Antoine, compliments of Steve Sillett). Right, Humboldt State University students Naomi Withers and Cameron Williams search a
complex redwood crown for salamanders. This search area is 60 meters above the ground. (Photographed by James C. Spickler).
Herpetological Conservation and Biology 1(1):16-26
19
and Van Pelt):
Total mass (kg) = 32.912 × mat volume + 0.0250 × maximum
frond length.
To better visualize individual tree crown complexity, we
generated three-dimensional models of tree crowns using
Microsoft Excel and the crown structure data (Sillett and Van
Pelt, unpubl. data). We overlaid locations of fern mats and
salamander captures on the crown models via their XYZ
coordinates (Fig. 1). We used this information to quantify
movements of salamanders captured more than once during the
study.
Capturing salamanders.To locate A. vagrans without
destructive sampling, we placed cover objects on fern mats
within each tree crown. We constructed cover objects from gray
fiberglass screening. We cut and folded materials to produce
flat envelope-like bags (hereafter ‘litter bags’) that were filled
with decomposing leaf litter and soil, producing both small (25
× 20 cm) and large (25 × 40 cm) bags. To limit introduction of
foreign materials to the canopy, only litter and soil from each
selected site were used to fill the bags.
Placement of litter bags was determined randomly. The total
surface area of a tree’s fern mats was calculated by summing the
surface areas of all the mats on the tree. Ten percent of the mat
area on each tree was covered such that half was covered by
each type of litter bag. The probability of an individual fern mat
being randomly selected for a given litter bag was proportional
to its surface area. Thus, some fern mats, especially large ones,
received multiple litter bags while others, especially small ones,
received none. The placement of individual litter bags on
selected fern mats was not done randomly. Instead, we spaced
the bags across the mats in an attempt to minimize the likelihood
of their being blown from the crown during storms. This
involved nestling the bags into relatively flat regions of the
mats. Wooden sticks were placed underneath each litter bag to
maintain crawl spaces for salamanders.
Besides litter bags we deployed cover boards, which were
crafted from pairs of 2-cm-thick boards cut into 25 x 25 cm
sections (Davis 1991). We placed boards together but
separated by parallel 1-cm-thick strips of wood that created a
crawl space for salamanders. Our cover boards were designed
to simulate preferred terrestrial habitats of A. vagrans: 6 mm
spaces between bark and heartwood with a smooth firm
surface (Davis 1991). This species is often found under the
splintered wood of recently fallen trees or exfoliating bark
(Davis 2002b; Stebbins 2003). We limited use of cover boards
for fear of causing injury to climbers and tourists visiting the
grove if the boards happened to fall from the trees. However,
we left two cover boards on a large fern mat in Prometheus
and one on a large fern mat in Iluvatar. These locations seemed stable
enough to prevent loss of the boards during storms. As an extra
precaution we equipped the boards with small lengths of cord anchored
to the tree.
Access restrictions.—Summer and spring observations were not
possible due to climbing restrictions to protect the nesting habitat of two
threatened species in the area: the Marbled Murrelet (Brachyramphus
marmoratus) and Northern Spotted Owl (Strix occidentalis caurina).
Thus, our field season was limited to the fall (late September) through
winter (end of January), during three field seasons from 2000 to 2002.
During these periods, we checked our cover objects 2-4 times per
month, weather permitting. We also made weekly checks of litter bags
and cover boards in Prometheus during the 2002-2003 field season, and
made one visit to Iluvatar during this time. During each visit, all cover
objects were checked. A description of any salamander activity, time
and location of each capture were recorded.
Marking salamanders.We anesthetized captured A. vagrans using
a pH neutral solution of MS-222 (3-aminobenzoic acid ethyl ester)
achieved by combining 1.0 g MS-222 + 2.4 g sodium bicarbonate
dissolved in 500 ml distilled water. Once salamanders were immobile,
they were permanently and uniquely marked under anesthesia with 1 x
2 mm fluorescent alpha-numeric tags (Northwest Marine Technologies,
Inc., Seattle, Washington, USA) injected subcutaneously on the ventral
side of the tail immediately posterior to the vent. Photographs of dorsal
patterns were taken of salamanders too small to be injected with tags.
Marked animals were returned to their point of capture once fully
recovered from the MS 222. We recorded snout to vent length (i.e.,
from tip of snout to anterior margin of vent), total length, number of
costal folds between adpressed limbs, weight (to the nearest 0.1 g), sex
if recognizable by secondary sexual characteristics (e.g., shape of head,
presence of mental glands, cirri, eggs in oviducts), and any injuries or
other identifying marks.
Data analyses.We used stepwise multiple regression analysis to
evaluate potential effects of individual fern mat characteristics on
TABLE 1. Summary of tree size, Polypodium scouleri fern mats, soil water storage, and salamander abundance in five redwood trees from Prairie Creek
Redwoods State Park, California. Soil water storage values are whole-tree annual averages derived from a model (Sillett and Van Pelt unpublished).
Salamander abundance is the number of Aneides vagrans captured on fern mats in each tree, excluding those captured with cover boards.
Tree: Rhea Demeter Kronos Iluvatar Prometheus
Height (m) 95.5 97.5 91.6 91.5 97.4
DBH (cm) 405 434 428 614 559
Main trunk volume (m3) 359.3 389.7 335.4 874.0 598.5
Reiterated trunk volume (m3) 1.2 20.2 30.5 162.5 63.1
Limb volume (m3) 1.5 6.4 14.5 24.6 3.2
Fern mat dry mass (kg) 205 39 275 249 352
Fern mat dry mass in crotches (kg) 8 6 18 97 249
Soil water storage (l) 1003 437 1561 1908 4416
Fern mat salamander abundance 2 3 8 7 14
TABLE 2. Estimated sizes of Aneides vagrans populations on large redwood trees
over two years derived from mark-recapture data using the Chapman (1951)
method (see Chao and Huggins 2005). Numbers in parentheses are one standard
error. Estimates are only for the portion of the arboreal population using fern
mats.
Salamander Abundance
Tree January 2002 January 2003
Prometheus 11 (0) 29 (8)
Iluvatar 11 (2) 20 (11)
Kronos 8 (4)
Five trees
combined 54 (15)
Spickler et al.—Aneides vagrans in Redwood Canopies September 2006
20
salamander abundance in those mats with cover objects (n = 65).
The following independent variables were included: percentage
of surface covered by litter bags, total area covered by litter
bags, total surface area, dry mass, and height above ground. The
number of cover boards on each fern mat (0, 1, or 2) was also
used as an independent variable to account for the potential
effects of this sampling technique. The dependent variable was
the number of salamander captures per mat.
We evaluated potential effects of fern mats and tree structure
on A. vagrans abundance using correlation analysis. Tree-level
independent variables (n = 5) included total fern mat mass (kg),
mass of fern mats in crotches, and the average amount of water
stored (l) in each tree’s fern mats throughout the year. This last
variable was derived from a canopy soil hydrology model
developed for the permanent reference stand that includes all of
the trees in this study (Sillett and Van Pelt, unpubl. data).
Structure variables included volumes (m3) of each tree’s main
trunk, reiterated trunks, and limbs. The dependent variable was
the number of marked animals per tree. We corrected for
sampling effort by dividing the actual number of visitations per
tree (n = 27–33) by the highest number of visitations for any
tree. We eliminated the potentially confounding effects of cover
boards by removing those two mats from the data set prior to the
analysis.
Tree-level salamander abundance was estimated with the
Chapman (1951) method (see Chao and Huggins 2005). We
used the unbiased estimator for population size (N):
1
1)1)(1(
+
++
=
R
CM
N
where M = number of individuals marked in the first sample, C
= total number of individuals captured in the second sample, and
R = number of marked individuals recaptured in the second
sample. For this analysis, we made the following assumptions:
1) sampling was random; 2) the population was closed (i.e., no
immigration, emigration, birth, or death) within each field
season; 3) all animals had the same chance of being caught in
the first sample; 4) marking individuals did not affect their
catchability; 5) animals did not lose marks between sampling
intervals; and 6) all marks were reported on discovery in the
second sample. We recognize that there are limitations to this
method (see Pollack et al. 1990) but our small samples did not
permit a more sophisticated approach. As a consequence we
consider these estimations only as first approximations of
salamander abundance in fern mats.
Other salamander observations.The inaccessibility of
study trees during the spring and summer greatly limited our
ability to make year-around observations of arboreal A. vagrans
activity. However, several relevant observations were made by
forest activists participating in “tree-sits” at other nearby
locations, and by scientists working in the canopy on research
unrelated to this study. We include a summary of these
anecdotal observations with our results because these accounts
fill gaps in our temporal record and provide documentation of
salamander presence in the canopy throughout the entire year.
RESULTS
Tree-level population estimates.A total of 55 captures were
made of 42 individual A. vagrans, including 13 recaptures. One
individual was captured five times, two individuals were
captured four times, three individuals were captured twice, and 36
individuals were captured only once. Captured individuals ranged from
1.3–7.1 cm in SVL, 2.4–14.7 cm in total length, and 0.1–5.9 g in mass.
Salamanders were found in all five study trees with the most captures in
Prometheus (n = 28) and the least in Rhea (n = 2). Small sample sizes
forced us to use entire field seasons as sampling intervals to make
population estimates for each tree. Thus, A. vagrans abundance was
estimated once for three trees (Prometheus, Iluvatar, Kronos) in January
2002 for animals marked in the first field season and marked or
recaptured in the second field season (8–11 individuals per tree), and
again for two trees (Prometheus and Iluvatar) in January 2003 for
animals marked in the second field season and marked or recaptured in
the third field season (20–29 individuals per tree, Table 2). There were
insufficient data to make any tree-level population estimates for two of
the trees (Demeter and Rhea). However, we combined data from all
five trees to calculate an estimate of 54 salamanders for these five tree
crowns collectively in January 2002 based on animals marked in the
first field season and marked or recaptured in the second field season
(Table 2).
Tree-level effects on salamander abundance.Based on correlation
analyses at the tree-level, there were two significant predictors of
salamander abundance per tree: average water storage by fern mats (r =
0.930, P = 0.022) and mass of fern mats in crotches (r = 0.885, P =
0.046). Our small sample size (n = 5 trees) prohibited further analyses
of tree-level effects for other fern mat variables (total fern mat mass,
proportion of total fern mat mass in crotches), and three structural
variables (main trunk volume, reiterated trunk volume, and limb
volume).
Effects of fern mat characteristics on salamander captures.Fern
mat-level effects on A. vagrans captures and recaptures were evaluated
separately for a total of 65 fern mats (i.e., only those with cover objects)
in five trees using regression analysis. Total number of A. vagrans
captured, including recaptures, was positively associated with number
of cover boards (R2 = 0.85, P < 0.0001), area covered by litter bags (R2
= 0.38, P < 0.0001), fern mat mass (R2 = 0.28, P <0.0001), and fern mat
area (R2 = 0.22, P < 0.0001). No associations were found between
captures and either the percentage of fern mat surface area covered by
litter bags (R2 = 0.002, P = 0.70) or height (R2 = 0.004, P = 0.62).
Stepwise multiple regression analysis revealed that number of cover
boards (adjusted R2 = 0.85, P < 0.00001), fern mat mass (cumulative R2
= 0.90, P < 0.00001), and height of fern mat (cumulative R2 = 0.91, P <
0.03) all accounted for significant amounts of variation in the number of
salamander captures.
The strongest variable affecting the number of A. vagrans captured
was not a physical characteristic of the fern mats, but was an artifact of
our sampling technique. Significantly more salamanders were captured
on fern mats with cover boards than on mats with only litter bags. In
Prometheus, the total number of captures on one fern mat was 15,
representing 5 individuals. All of the captures were made in two cover
boards, although 8 litter bags occurred in close proximity to the cover
boards. Nine of the 15 captures were recaptures, including four of a
single large male who had apparently taken up residence in an area that
included both of the cover boards, which were located < 0.5 m apart.
He was captured during all 3 years of the study, and on several
occasions he was found with other salamanders. On one fern mat in
Iluvatar, there were 9 captures representing seven individuals. Seven of
these were made in a cover board, while the remaining two were made
under a litter bag located 75 cm away.
Movement of recaptured salamanders.We found no evidence of
among-tree movements of marked salamanders, via interacting crowns
Herpetological Conservation and Biology 1(1):16-26
21
or the ground. Of the 13 recaptures, 12 were of individuals
found in the same locations as their initial captures. The single
exception was a juvenile A. vagrans (1.2 g, SVL= 4.35 cm)
found under a litter bag (first capture) and then recaptured a
week later on the surface of a fern mat 7.5 m higher in the tree.
Seasonal activity.Our limited field season precluded
observations of seasonal differences in movement and habitat
use, but based on our findings and several anecdotal
observations made outside of our field seasons (see below), it
appears that at least some individual A. vagrans occupy the
forest canopy throughout the year.
Other observations.The few spring and summer
observations were often made while canopy researchers were
conducting surveys for protected species (Marbled Murrelet and
Spotted Owl). Also, salamander observations were made by
non-scientists illegally occupying trees to protect them from
logging. It is understandable that the protection of threatened
species takes priority over new research dealing with a
salamander that appears to be abundant, at least in terrestrial
habitats, but the lack of data for these seasons left us with
several unknowns concerning the life history and ecology of A.
vagrans in redwood forests. The following observations may
help us to understand A. vagrans behavior during these periods.
The willingness of tree sitters to stay aloft for extended
periods enables them to make observations that scientists
working under research permits cannot afford to do. In the
spring of 2002, an activist designated as Remedy began a tree-sit
on private timber lands. Remedy, along with other activists,
established sleeping platforms in several large redwoods near
Freshwater, in coastal Humboldt County, California. Remedy
remained aloft for nearly a year before being forcibly removed
and arrested for trespassing. In that time period she made
numerous observations of a pair of wandering salamanders.
On seven occasions from April to September, Remedy
observed the “same pair” of wandering salamanders moving
within an area around a small cavity located 3 m from her living
platform. The original leader of the tree had broken at an
approximate height of 40 m; the living platform was located a
few meters below the break. The loss of the leader occurred at
least 100 years before, and two reiterated trunks had replaced it.
A zone of decaying wood that had formed around the break
created the cavity that the salamanders occupied. The same
cavity was also shared by a small “tree squirrel,” probably a
Douglas’ Tree Squirrel (Tamiasciurus douglasii) or a Northern
Flying Squirrel (Glaucomys sabrinus). A P. scouleri fern mat
occupied the top of the broken trunk.
Remedy often observed the salamanders moving in close
proximity to each other, but they appeared to be “moving
independently as if unaware of each other.” Most of the
salamander activity was limited to the area on and around the
fern mat, but on two occasions a salamander moved out along
branches and continued to the outer crown where it could no
longer be seen. All observations were made during early
evening and under similar microclimatic conditions: dry
substrate with elevated air humidity. Conditions were described
as “warm and muggy, perfect weather for flying insects.” One
stated impression was that the salamanders were more affected
by temperature than by moisture as no animals were observed
moving during the rain or immediately thereafter. There was
limited flying insect activity during and immediately after rain
storms. Observations were always made during calm
conditions with little or no wind. The two salamanders were
observed throughout the spring and summer with the last observation
occurring on 21 September 2002, when “evenings became too cold for
foraging.”
Remedy reported an A. vagrans eating while in the canopy. One
evening, she noted an insect, a “winged termite,” alight on a small
branch approximately 30 cm from the salamander. The salamander
then rapidly moved to the insect, which it ate without hesitation. After
a moment, the salamander continued moving along the branch to the
outer crown.
Similar observations were made by another activist, Raven,
participating in a tree-sit in the Van Duzen watershed in Humboldt
County. Raven made several observations of a pair of A. vagrans
foraging near his sleeping platform. He also described how A. vagrans
activity decreased along with decreasing nighttime temperatures as
autumn and winter approached. On 2 February 2003, he observed a pair
of A. vagrans move on to his platform. He watched them for several
minutes before they continued off into the darkness.
On 17 September 2002 at 0800 hrs, one of us (Stephen Sillett) and his
graduate student (A. Ambrose) observed an adult A. vagrans while
crown-mapping a large redwood in Humboldt Redwoods State Park.
The observation was made during warm conditions with high air
humidity and low cloud cover; the tree’s bark was dry. We observed a
single adult A. vagrans moving vertically along the trunk at a height of
93 m above ground. The salamander’s path was exposed with no soil or
obvious cover nearby. The nearest area of apparent cover was in a
cavity of dead wood located 100.6 m above the ground, but the surface
of this site was also exposed and dry. Obvious fissures and crevices in
the decaying wood, however, likely allow such animals to enter and
retire within damp cavities.
We also have made incidental observations of A. ferreus, a close
relative of A. vagrans. On three separate occasions in 2002, one of us
(James Spickler) and N. Bowman observed adult A. ferreus while
studying the nesting behavior of the red-tree vole (Arborimus pomo) in
old-growth Douglas-fir forests of coastal Oregon (BLM forest lands,
Salem and Eugene Districts). Observations were made in the summer
(July-August), midday during periods with high humidity and on moist
substrates. In all cases, salamanders were inactive and hidden within
the stick nests of a western grey squirrel (Sciurus griseus). Two of
these salamanders were found in an active nest containing fresh feces
and elevated temperatures from the recently departed rodent’s body.
In 1993, Stephen Sillett observed an A. ferreus while conducting
canopy research in a 700-year-old Douglas-fir forest (Middle Santiam
Wilderness Area, Willamette National Forest, Willamette County,
Oregon; see Sillett 1995). While climbing in a large Douglas-fir tree
adjacent to a 30-year-old clearcut, he found an adult salamander under
moss (Antitrichia curtipendula) on a large branch approximately 30 m
above the ground. After being disturbed, the salamander moved
horizontally across the branch and retreated under a bark flake on the
tree trunk. The observation was made midday during the dry season
(early autumn), and the moss mat was “merely damp.”
DISCUSSION
Plethodontid salamanders are unique in that they are the only
salamander family to have invaded the tropics, where many species
occupy arboreal niches (Lynch and Wake 1996). However, in spite of
the high number of species displaying arboreal habits in tropical forests,
little is known about this phenomenon beyond a few anecdotal accounts
(e.g., Good and Wake 1993; McCranie and Wilson 1993). Our results
here provide information on a new niche dimension for a North
American temperate zone plethodontid salamander, the resident use of
arboreal habitats in redwood forest canopies by Aneides vagrans.
Like other plethodontid salamanders, A. vagrans is lungless and
respires exclusively through its skin and buccopharynx. Presumably,
Spickler et al.—Aneides vagrans in Redwood Canopies September 2006
22
this requires the maintenance of skin moisture to facilitate
respiratory gas exchange (Shoemaker et al. 1992). The skin of
most amphibians is highly permeable to liquid and gas, allowing
for moisture exchange rates similar to those of standing water
(Spotila and Berman 1976). To avoid fatal desiccation,
amphibians have developed a variety of behavioral and
physiological means by which to control water loss (Shoemaker
et al. 1992). Plethodontid salamanders select habitats with
suitable microsites that retain relatively high moisture contents
as the macrosite begins to dry (Thorson 1955; Cunningham
1969; Ovaska 1988; Cree 1989; Shoemaker et al. 1992). This
desiccation-avoidance behavior has been observed in terrestrial
A. vagrans (Davis 2002b).
Our correlation analysis of tree-level effects on salamander
abundance highlights the importance of water storage in soils
beneath epiphytes and location of this material within the crown
(e.g., in crotches). Soils on limbs drain faster than those in
crotches (Ambrose 2004; Enloe et al. 2006) and thus may
become too dry for perennial occupancy by salamanders.
Microclimate data from fern mats show that crotches have more
stable moisture and temperature regimes than branches or limbs
(Ambrose 2004; Sillett and Van Pelt, unpubl. data). Compared
to those on branches or limbs, fern mats in crotches hold more
water per unit mass and store water longer (Sillett and Van Pelt,
unpubl. data). Furthermore, soils in crotches have higher bulk
densities and lower hydraulic conductances than soils on
branches or limbs (Enloe et al. 2006), providing relatively stable
refugia from desiccation during the dry season. Trees with soil
in deep crotches likely provide suitably moist arboreal habitats
for the year-round occupancy of old-growth redwood forest
canopies by A. vagrans, enabling this salamander to breed and
potentially live its entire life within tree crowns.
The effects of fern mat size and height on salamander
captures are ecologically interpretable. The positive correlation
between fern mat size and A. vagrans abundance can be
attributed to the larger surface area available for foraging, higher
water-holding capacity, and greater internal complexity of larger
fern mats. Although the arboreal feeding habits of A. vagrans
have not been studied, the salamanders probably take prey from
fern mats. Fern mat surfaces (at least seasonally) have more
invertebrate biomass than other surfaces (e.g., bark and foliage)
in redwood crowns (Jones 2005). In fact, the mites and
collembolans inhabiting fern mats experience population
explosions during the wet season, and have densities similar to
those observed in terrestrial habitats under similar conditions
(Jones 2005).
Larger, deeper fern mats have greater water storage and
slower rates of desiccation than smaller mats (Ambrose 2004),
thus providing more stable, moist microclimates conducive to A.
vagrans habitation. As a fern mat increases in size, new roots
and rhizomes grow to replace the old ones, which subsequently
decay. Although debris from litter fall, especially tree foliage, is
a major component of the P. scouleri fern mats, the majority of
organic material in these mats comes from P. scouleri itself,
especially humus derived from decaying roots and rhizomes
(Sillett and Bailey 2003). Dead, decomposing rhizomes leave
behind “tunnels” in the soil. Larger debris (e.g., branches) that
falls onto fern mats can also create tunnels and internal cavities
as it is covered by other debris and begins to decompose. On
three occasions, Sillett and Bailey (2003) found A. vagrans
occupying interstitial spaces in P. scouleri mats (mats were
being harvested for the development of equations to predict fern
mass). Also, an egg cluster of A. vagrans was found within a P.
scouleri mat on a freshly fallen old-growth redwood (Welsh and Wilson
1995). These observations suggest that the tunnels and cavities in fern
mats are used by A. vagrans, and it is likely that they are important
refugia, but the fragile nature of the substrate makes searching the
tunnels nearly impossible without permanently altering the habitat.
The negative effect of fern mat height on salamander captures can be
attributed to the varying microclimates at different heights within a
forest canopy. During periods with no precipitation, the upper canopy
receives more light and wind, and the air is less humid compared to the
lower canopy (Parker 1995, Sillett and Van Pelt, unpubl. data).
Therefore, fern mats in the upper canopy, regardless of size, are
subjected to more frequent and severe periods of desiccation than those
in the lower canopy. In redwood forest canopies this effect can be seen
in P. scouleri itself. Although fern mat size is not correlated with
height, the size and shape of fronds become progressively smaller with
increasing height in the forest (Sillett and Bailey 2003). The negative
effect of height on number of A. vagrans captured can be attributed to
the less stable microclimate of upper canopy fern mats compared to
those in the lower canopy. Fern mats higher in a tree may be important
for salamanders foraging during wet periods, but the prolonged
occupation of these sites may be risky during dry periods. This idea is
supported by our discovery of two mummified individuals near the tops
of two trees over 90 m tall (see also Maiorana 1977).
Dead wood may represent another important habitat for arboreal
salamanders in redwood forests. At the forest level, the average water
storage in dead wood (16,500 l ha-1) rivals the amount stored in canopy
soil (19,700 l ha-1), and seasonal variation in dead wood water storage is
less than that in soils on branches and limbs (Sillett and Van Pelt,
unpubl. data). Even though we did not quantify salamander abundance
in dead wood habitats, a number of anecdotal observations suggest that
A. vagrans use dead wood and hollow cavities. The highest observation
of this species ever made (93 m) was of a salamander climbing upwards
on a late summer morning towards the dead, broken top of a large
redwood nearly lacking vascular epiphytes and soil. It is likely that
large populations of A. vagrans reside within hollow trunks of standing
redwoods in old-growth forests.
Movement and territoriality.If a salamander finds a habitat that
has a favorable moisture regime and sufficient prey availability, it
would be advantageous for the animal to stay in that habitat or return to
it frequently (Jaeger 1980). Terrestrial A. vagrans move only short
distances, are site-tenacious, and return periodically to particular
habitats within their home range (Davis 2002a). Our canopy findings
parallel these terrestrial observations.
On 6 occasions we captured more than one salamander on a fern mat.
Twice we found two males in a cover board with a single female. We
also found two females together with no male present and two males
together with no female present. Twice we found a pair of salamanders
on the same fern mat but not within the same cover board: a male with
a female and a male with another male. Males did not appear to be
defending females from other males, and neither sex appeared to be
defending a particular site, both of which are major components of
territorial behavior (Brown and Orians 1970; Jaeger et al. 1982; Mathis
et al. 1995). Similar behaviors were observed in terrestrial A. vagrans
on Vancouver Island, British Columbia (Davis 2002a). Although
arboreal A. vagrans in redwood forests appear to be acting similarly to
terrestrial individuals in British Columbia, we did not sample during
either the breeding season (presumably spring) or the summer.
Arboreal A. vagrans may behave differently during certain times of the
year if resources, such as nest sites, prey items, or moist habitats,
become limited.
Herpetological Conservation and Biology 1(1):16-26
23
Seasonality.The seasonal restrictions on canopy research in
old-growth redwood forests prevented us from sampling
salamanders for eight months of the year, including the summer
dry season. When considering the hydric constraints of
plethodontid salamanders, it is likely that A. vagrans would be
less active on forest canopy surfaces during the dry season.
Anecdotal observations of A. vagrans, as well as observations of
other species of Aneides, suggest otherwise however. Arboreal
Aneides may be most active during the drier and warmer spring
and summer given the strong marine influences that contribute
to mild temperatures and high relative humidity during these
seasons in the coastal redwood forest (Sawyer et al. 2000).
Green salamanders (Aneides aeneus) use arboreal habitats
seasonally (Waldron and Humphries 2005). These animals
over-winter in rock outcrops and migrate into woody or arboreal
habitats (primarily hardwoods) during the onset of spring. They
remain in these habitats throughout the summer and breeding
season before returning to rock outcrops sometime in October
and November. Green Salamanders prefer larger (in diameter)
and more complex trees having a variety of visible cavities. On
dry days individuals are often found under the flaky and
furrowed bark of several different tree species. The maximum
height above the ground where Green Salamanders have been
observed is 21 m at the mouth of a tree hollow (Waldron and
Humphries 2005). Gordon (1952) noted a decrease in Green
Salamander abundance during the dry season, but Waldron and
Humphries (2005) demonstrated that the salamanders may be
climbing into the canopy where they remain throughout the
summer and cannot be easily detected from the ground.
It is unlikely that A. vagrans utilizes arboreal habitats
seasonally like A. aeneus. Anecdotal observations do not
support such a scenario but instead suggest year-round
residency. At most, A. vagrans may shift its use of particular
microhabitats within the canopy, but it remains unclear which
suitably moist locations might be preferred during different
seasons.
Effects of tree- and fern mat-level variables on
salamanders.Our mat-level analysis indicated an effect of
cover boards on number of salamanders. Nearly half of the A.
vagrans captured during our study were found in cover boards
even though their use was quite limited. By placing cover
boards on top of fern mats we may have created a preferred
habitat type. This assertion is supported by observations that
dead wood substrates were favored by terrestrial A. vagrans
populations in Vancouver Island, British Columbia (Davis
2002b). It is unclear whether the salamanders captured in our
cover boards were residents of the fern mat on which the boards
were placed, originally residing in the tunnels and other
complexities of the fern mat, or if placing the cover boards on
the fern mat created a habitat allowing foraging individuals from
other parts of the tree the opportunity to stay and take up
residence. The paucity of recaptures under litter bags suggests
that A. vagrans prefers crevices but will use litter bags
opportunistically for cover while foraging.
Future research.Future studies should examine how A.
vagrans uses other habitats besides fern mats, since the
preponderance of cover board captures as well as anecdotal
observations suggest that A. vagrans inhabits crevices, cavities,
and lodged woody debris at least as much as it does soil beneath
ferns (P. scouleri). Crevices and cavities are difficult to search
manually in a non-destructive fashion, and we discourage this
activity. Placing cover boards adjacent to these sites would
allow capture of salamanders coming out to forage on other tree
surfaces without permanently altering the habitat. Cover boards also
create new habitats within tree crowns for salamanders and their prey.
The entrance to natural and artificial crevices and cavities could be
monitored continuously (even during summer months when canopy
access is restricted) via motion-sensitive, infrared video cameras.
Microclimate data could also be compared to videos to determine
preferred conditions for foraging and also to document salamander
behavior throughout the annual cycle. Identification of salamanders via
videos would be possible using a visual implant fluorescent elastomer
marking technique and by marking individuals on their dorsal surfaces.
Hopefully our discovery of resident arboreality in Aneides vagrans
will trigger a renewed interest in studying adaptations of plethodontid
salamanders to the use of arboreal habitats. For example, the recently
described modification (Sapp 2002) of the typical plethodontid
courtship tail-straddling walk (Houck and Arnold 2003) from linear to
circular in the genus Aneides may be an adaptation to arboreality.
Conservation implications.Resident populations of arboreal
salamanders in old-growth forests may be top predators of diverse,
heterotrophic communities fueled by the productivity of epiphytes and
the trees themselves. Such ecosystems appear to be lacking in younger
forests regenerating on logged-over land. Only 4% of the original old-
growth redwood forests remain, and second-growth forests originating
before 1930 are scarce (Noss 2000). Nearly all regenerating redwood
forests are younger than rotation age (~ 50 years) and consisting of trees
less than 40 m tall with small branches. As a consequence of their
simple structure, the biological diversity of young redwood forests is
low, and many old-growth-associated plants and animals are now
restricted to a few National and State Parks (Sawyer et al. 2000;
Cooperrider et al. 2000). Redwood forests capable of supporting
arboreal salamanders are rare outside of these Parks. Even within the
Parks, epiphytic vascular plants and associated soil communities do not
occur in the crowns of small trees despite their proximity to large trees,
because the structural complexity (e.g., large limbs and reiterated
trunks) necessary to support these organisms develops very slowly.
Thus, the arboreality of A. vagrans in redwood forests may be a
phenomenon restricted to a tiny portion of the landscape. Further
investigations to establish a basis for the conservation of A. vagrans and
associated organisms in protected forests are warranted.
Acknowledgments.—We thank the U.S. Forest Service’s Pacific
Southwest Research Station, Save-the-Redwoods League, and Global
Forest Science (GF-18-1999-65) for grants supporting this research.
We also thank Cameron Williams, Marie Antoine, and Nolan Bowman
for assistance with fieldwork. We appreciate the co-operation of the
California Department of Fish and Game (permit SCP#003419) and the
Redwood National and State Parks (permit REDW1999Sillett) in
support of this research. This project was conducted under Humboldt
State University IACUC permit number 00/01.B.31.
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A Wandering Salamander (Aneides vagrans) from Humboldt County, California (United States). (Photograph by: William Leonard, ©2004. All
Rights Reserved.)
Spickler et al.—Aneides vagrans in Redwood Canopies September 2006
2
JAMES C. SPICKLER is the senior biologist for Eco-Ascension Research
and Consulting (eco-ascension.com). He received his B.S. in Wildlife,
and M.A. in Biology from Humboldt State University, California. His
research interests include herpetology and temperate/tropical forest
canopy ecology. This publication represents research conducted at
Humboldt State University for his M.A. degree in Biology.
STEPHEN C. SILLETT is a Professor of Botany and the Kenneth L. Fisher Chair in
Redwood Forest Ecology at Humboldt State University. He received his B.A. in
Biology at Reed College, M.Sc. in Botany at University of Florida, and Ph.D. in
Botany and Plant Pathology at Oregon State University. Steve's research focuses
on the linkages between structure and biodiversity in forest canopies as well as
the biophysical and ecological constraints on maximum tree height.
SHARYN B. MARKS is a Professor of Zoology at Humboldt State
University. She received her B.A. in Biological Sciences at University
of Chicago, and her Ph.D. in Integrative Biology at the University of
California at Berkeley. Sharyn’s research focuses on integrating studies
of amphibian ecology with the management of natural resources to
promote amphibian population viability.
HARTWELL H. WELSH, JR. is a research wildlife ecologist with the Pacific Southwest
Research Station of the U. S. Forest Service. He is stationed at the Redwood Sciences
Laboratory in Arcata, California. He received a B.S. in Zoology from the University of
California at Berkeley, M.S. in Wildlife Biology from Humboldt State University, and
Ph.D. In Wildlife Ecology from University of California at Berkeley. His current
research interests include: (1) the relationships of forest structure and riparian attributes
to the distribution and abundance of forest herpetofauna; (2) the use of amphibians as
indicators of ecosystem health and integrity; and (3) the mechanisms of amphibian
declines.
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... Many species of salamander occupy arboreal habitats year-round, including members of the genera Aneides, Bolitoglossa, Chiropterotriton, Dendrotriton, Ixalotrition, Nototriton, Pseudoeurycea, and Thorius (McEntire, 2016;Spickler et al., 2006;Wake, 1987). Even primarily terrestrial and semi-aquatic species have been observed clinging to and climbing up tree trunks, plant stems, cave walls, talus slopes, and vertical rock faces (Bradley & Eason, 2018;Camp et al., 2013;Crawford & Peterman, 2013;Gorman & Camp, 2006;Huheey & Brandon, 1973;Lunghi et al., 2017;McEntire, 2016;Spickler et al., 2006;Waldron & Humphries, 2005). ...
... Many species of salamander occupy arboreal habitats year-round, including members of the genera Aneides, Bolitoglossa, Chiropterotriton, Dendrotriton, Ixalotrition, Nototriton, Pseudoeurycea, and Thorius (McEntire, 2016;Spickler et al., 2006;Wake, 1987). Even primarily terrestrial and semi-aquatic species have been observed clinging to and climbing up tree trunks, plant stems, cave walls, talus slopes, and vertical rock faces (Bradley & Eason, 2018;Camp et al., 2013;Crawford & Peterman, 2013;Gorman & Camp, 2006;Huheey & Brandon, 1973;Lunghi et al., 2017;McEntire, 2016;Spickler et al., 2006;Waldron & Humphries, 2005). Up to 45% of nonfully aquatic plethodontid salamanders have been documented climbing in their natural environments (McEntire, 2016). ...
... Reasons for engaging in climbing up and clinging on plants and rocks include finding food (Jaeger, 1978;Legros, 2013) or escaping larger predatory species (Crawford & Peterman, 2013). Elevated, sheltered habitats or caves also form a vital refuge from unfavorable temperature or humidity conditions for these desiccation-prone species (Forsman & Swingl, 2007;Gorman & Camp, 2006;Lunghi et al., 2017;Spickler et al., 2006;Wake 2014) and may be used in nesting (Lunghi et al., 2014(Lunghi et al., , 2015Myer, 1958;Spickler et al., 2006;Waldron & Humphries, 2005). Thus, it is clear that access to these climbing-accessible environments provides numerous benefits across salamander species. ...
Article
Full-text available
The interaction between morphology, performance, and ecology has long been studied in order to explain variation in the natural world. Within arboreal salamanders, diversification in foot morphology and microhabitat use are thought to be linked by the impact of foot size and shape on clinging and climbing performance, resulting in an ability to access new habitats. We examine whether various foot shape metrics correlate with stationary cling performance and microhabitat to explicitly quantify this performance gradient across 14 species of salamander, including both arboreal and nonarboreal species. Clinging performance did not correlate with foot shape, as quantified by landmark-based geometric morphometrics, nor with microhabitat use. Mass-corrected foot centroid size and foot contact area, on the other hand, correlated positively with clinging performance on a smooth substrate. Interestingly, these foot variables correlated negatively with clinging performance on rough substrates, suggesting the use of multiple clinging mechanisms dependent upon the texture of the surface. These findings demonstrate that centroid size and foot contact area are more functionally relevant for clinging in salamanders than foot shape, suggesting that foot shape need not converge in order to achieve convergent performance. More broadly, our results provide an example of how the quantification of the performance gradient can provide the appropriate lens through which to understand the macroevolution of morphology and ecology.
... Investigators have developed sampling protocols for forest canopies. However, focused canopy sampling techniques, such as the popular single rope technique (Moffett and Lowman, 1995), are time-consuming and require specialized equipment and training, and in the case of bromeliads, sampling is typically destructive (Spickler et al., 2006;McCracken and Forstner, 2008;Brown et al., 2018). Typically, bromeliads are removed from trees and dissected to facilitate the collection of herpetofauna (McCracken and Forstner, 2008;García González, 2014). ...
... Although some frogs and lungless salamanders have occasionally been found .30 m above the ground (Spickler et al., 2006;McCracken and Forstner, 2008), sampling in the first ten meters of the trees may cover the largest proportion of the diversity of arboreal amphibians, since in this portion species from the ground, understory, and upper canopy can occur (Basham et al., 2019). For example, in a semi-deciduous dry forest in Cuba, amphibians and reptiles in tank bromeliads were found below 6 m height, and almost three-quarters of all the occupied bromeliads were even below 3.2 m (García González, 2014). ...
... Similarly, the effects of host tree identity, bromeliad species, and tank size could be investigated, and amphibians can be marked using new technologies (Courtois et al., 2013) to investigate their movement along the trees and to estimate population sizes. Spickler et al. (2006) provide an example of this in their study about the North American salamander Aneides vagrans. Moreover, because amphibians were found using tank bromeliads most frequently in cloud forests, where isolation and humidity are high and these plants typically reach their maximum abundances (Benzing, 1990;Hietz and Hietz-Seifert, 1995;Gómez-González et al., 2017), bromeliad inspections in this ecosystem should be considered an essential part of amphibian surveys. ...
Article
Bromeliads are recognized as vital habitats for arboreal amphibians. However, these plants are often not included in traditional amphibian surveys. Furthermore, focused canopy sampling techniques are time-consuming, require specialized equipment and training, and, in the case of bromeliads, sampling is typically destructive. In this study, we developed and tested a new passive sampling technique for amphibians in bromeliads, which can be easily implemented in common amphibian surveys in the Neotropics. Our study was conducted in five different forests along an elevation gradient (0–2,200 m a.s.l.) in the central region of Veracruz, Mexico. In each forest, 15 tank bromeliads were relocated on large trees at 1.5 m above the ground (n = 75) by fastening them onto metal rings attached to the trees. Over a period of one year, these bromeliads were inspected monthly for amphibians. In total, we recorded 34 individuals belonging to eight species, including small and rare species that are normally difficult to find in the field. This technique appears to be effective in detecting frogs and salamanders across a range of ecosystems, especially in the cloud and mangrove forest where they were found more frequently throughout the year. Bromeliad relocation represents an alternative sampling technique for arboreal amphibians, which reduces the number of bromeliads that have to be sacrificed, requires few resources and minimal prior knowledge, and can be implemented effectively in studies that need repeated sampling through time.
... Species from the genera Bolitoglossa, Chiropterotriton, Dendrotriton, Ixalotriton, Nototriton, Pseudoeurycea and Thorius live in arboreal neotropical habitats in Mexico, and Central and South America (McEntire, 2016;Wake, 1987). In the USA, salamanders of the genus Aneides occupy arboreal habitats seasonally, and Aneides vagrans has been documented climbing to 93 m, living year-round in the fern mats of old-growth redwood trees (McEntire, 2016;Spickler et al., 2006). Scansoriality is even more widespread within the family. ...
... Scansoriality is even more widespread within the family. In addition to the scansorial cave-dwellers Chiropterotriton magnipes and some Hydromantes species, up to 45% of terrestrial and semiaquatic species have been documented climbing on temporal scales ranging from short periods of nocturnal foraging up plant stems to year-round occupation of tree trunks, rock crevices, tallus slopes, and cave walls (Bradley and Eason, 2018;Camp et al., 2013;Crawford and Peterman, 2013;Gorman and Camp, 2006;Huheey and Brandon, 1973;Lunghi et al., 2017;McEntire, 2016;Spickler et al., 2006;Waldron and Humphries, 2005). ...
... In the Pacific Northwest, where arboreal Aneides species live, Dicamptodon salamanders prey on other amphibian species (Bury, 1972), and climbing may provide one means of avoiding predation. Climbing rock faces, tree trunks and cave walls may allow salamanders to find nest sites in cracks (Lunghi et al., 2014(Lunghi et al., , 2015Myer, 1958;Spickler et al., 2006;Waldron and Humphries, 2005). Eurycea and Plethodon species have been documented climbing plant stems and tree trunks at night to forage for insects (Jaeger, 1978;Legros, 2013). ...
Article
Plethodontid salamanders inhabit terrestrial, scansorial, arboreal, and troglodytic habitats in which clinging and climbing allow them access to additional food and shelter as well as escape from unfavorable temperature and moisture conditions and ground-dwelling predators. Although salamanders lack claws and toe pads found on other taxa, they successfully cling to and climb on inclined, vertical, and inverted substrates in nature. Maximum cling angle was tested on smooth acrylic, and the relationship between cling angle, body mass, and surface area of attachment (contact area) was investigated. This study found that many salamander species can cling fully inverted using only a portion of their ventral surface area to attach. Salamanders fall into three functional groups based on mass and maximum cling angle: (1) high performing, very small salamanders, (2) moderately high performing small and medium-sized salamanders, and (3) low performing large salamanders. They show significant differences in maximum cling angle, even between species of similar mass. In species of similar mass experiencing significantly different detachment stress (resulting from significantly different contact area), differences in morphology or behavior affect how much body surface is attached to the substrate. High performance in some species, such as Desmognathus quadramaculatus, is attributable to large contact area; low performance in a similarly sized species, Ensatina eschscholtzii, is due to behavior which negatively impacts contact area. There was not clear evidence of scaling of adhesive strength with increasing body size. Salamander maximum cling angle is the result of morphology and behavior impacting the detachment stresses experienced during clinging.
... Plethodontid salamanders access elevated and vertical habitats (McEntire 2016) and have been documented climbing on tree trunks, cave walls, and rock faces, in addition to surmounting obstacles such as boulders, tree trunks, and steep slopes while traversing forest floors, streambeds, and mountainsides (Wake 1987;Spickler et al. 2006;Camp et al. 2014). Climbing provides access to elevated or sheltered habitats where the temperature or humidity may be more suitable for adults or their offspring (Waldron and Humphries 2005;Spickler et al. 2006;Lunghi et al. 2014Lunghi et al. , 2017. ...
... Plethodontid salamanders access elevated and vertical habitats (McEntire 2016) and have been documented climbing on tree trunks, cave walls, and rock faces, in addition to surmounting obstacles such as boulders, tree trunks, and steep slopes while traversing forest floors, streambeds, and mountainsides (Wake 1987;Spickler et al. 2006;Camp et al. 2014). Climbing provides access to elevated or sheltered habitats where the temperature or humidity may be more suitable for adults or their offspring (Waldron and Humphries 2005;Spickler et al. 2006;Lunghi et al. 2014Lunghi et al. , 2017. Climbing also allows some species to move out of the reach of ground-dwelling predators or competitors (Bury 1972;Huheey and Brandon 1973;Crawford and Peterman 2013). ...
Article
Synopsis Animals clinging to natural surfaces have to generate attachment across a range of surface roughnesses in both dry and wet conditions. Plethodontid salamanders can be aquatic, semi-aquatic, terrestrial, arboreal, troglodytic, saxicolous, and fossorial and therefore may need to climb on and over rocks, tree trunks, plant leaves, and stems, as well as move through soil and water. Sixteen species of salamanders were tested to determine the effects of substrate roughness and wetness on maximum cling angle. Substrate roughness had a significant effect on maximum cling angle, an effect that varied among species. Substrates of intermediate roughness (asperity size 100–350 µm) resulted in the poorest attachment performance for all species. Small species performed best on smooth substrates, while large species showed significant improvement on the roughest substrates (asperity size 1000–4000 µm), possibly switching from mucus adhesion on a smooth substrate to an interlocking attachment on rough substrates. Water, in the form of a misted substrate coating and a flowing stream, decreased cling performance in salamanders on smooth substrates. However, small salamanders significantly increased maximum cling angle on wetted substrates of intermediate roughness, compared with the dry condition. Study of cling performance and its relationship to surface properties may cast light onto how this group of salamanders has radiated into the most speciose family of salamanders that occupies diverse habitats across an enormous geographical range.
... Little is understood about the degree of arboreality of many plethodontids, but for those that do climb and occupy arboreal niches, jumping could be an efficient approach to descend in response to environmental or predatory cues. Scansorial plethodontids, some of which are known to utilize arboreal habitats and elevated niches (Van Denburgh, 1916;Leonard, 1993;Spickler et al., 2006;McEntire, 2016), often have longer limbs and digits compared with more fossorial plethodontids (Stebbins, 2003;Petranka, 2010). Given these differences in morphology and habitat use from more fossorial plethodontids, it stands to reason that arboreal plethodontids may differ in jumping Aneides, a scansorial and arboreal genus of plethodontid salamander, is known to utilize elevated niches including tree canopies, snags and stumps, and crevices of rocky outcrops (Stebbins, 2003). ...
... Given these differences in morphology and habitat use from more fossorial plethodontids, it stands to reason that arboreal plethodontids may differ in jumping Aneides, a scansorial and arboreal genus of plethodontid salamander, is known to utilize elevated niches including tree canopies, snags and stumps, and crevices of rocky outcrops (Stebbins, 2003). Aneides vagrans is known to occupy the crowns of the world's tallest trees, with sightings of individuals up to 88 m off the forest floor (Spickler et al., 2006). Its relatively long limbs and digits likely contribute to its impressive climbing abilities (Stebbins, 2003;Petranka, 2010) and theoretical models predict that quadrupeds with relatively long hindlimbs should exhibit high takeoff velocities and jump farther (Alexander, 1968;Bennet-Clark, 1977;Emerson, 1985;Harris and Steudel, 2002). ...
Article
Jumping performance can have important implications for an animal's fitness by expanding its ability to evade predators and move between microhabitats. Jumping in terrestrial plethodontid salamanders is achieved through lateral bending and rapid unbending of the trunk, an action powered by axial musculature. Arboreal plethodontids, some of which are known to occupy tree crowns, tend to have more robust limbs and longer digits, which may affect their jumping kinematics and performance. We examined jumping kinematics in ten species of plethodontid salamanders, including four arboreal species of the genus Aneides, using high speed imaging and kinematic analysis. Salamanders of the genus Aneides exhibit lower takeoff velocities when compared with the terrestrial plethodontids Eurycea, Desmognathus, and Plethodon, possibly due to reduced trunk bending. Aneides also exhibit higher frequencies of two-footed takeoffs, and often orient their feet to launch from vertical surfaces when presented with the option. This suggests an alternative jumping behavior in salamanders that may reflect an arboreal lifestyle. All plethodontid species examined displayed distinctive in-air parachute postures after 45-100% of descending jumps, with Aneides showing the highest frequency of this behavior.
... Our hybrid model projections indicate annual mean temperature and environmental seasonality (both temperature and precipitation) play a major role in shaping the green salamander distribution. Green salamanders are known to use and breed in moist rock crevices (Gordon 1952), and moisture appears to be a limiting factor in the distribution of other Aneides species (Rosenthal 1957, Spickler et al. 2006, Haan et al. 2007. Interestingly, both the CCSM4 and the Hadley GCMs predict a wetter future within the BRE (Supporting information), yet only the Hadley scenarios were associated with an increase in habitat suitability. ...
Article
Full-text available
Rapid global change has increased interest in developing ways to identify suitable refugia for species of conservation concern. Correlative and mechanistic species distribution models (SDMs) represent two approaches to generate spatially‐explicit estimates of climate vulnerability. Correlative SDMs generate distributions using statistical associations between environmental variables and species presence data. In contrast, mechanistic SDMs use physiological traits and tolerances to identify areas that meet the conditions required for growth, survival and reproduction. Correlative approaches assume modeled environmental variables influence species distributions directly or indirectly; however, the mechanisms underlying these associations are rarely verified empirically. We compared habitat suitability predictions between a correlative‐only SDM, a mechanistic SDM and a correlative framework that incorporated mechanistic layers (‘hybrid models'). Our comparison focused on green salamanders Aneides aeneus, a priority amphibian threatened by climate change throughout their disjunct range. We developed mechanistic SDMs using experiments to measure the thermal sensitivity of resistance to water loss (ri) and metabolism. Under current climate conditions, correlative‐only, hybrid and mechanistic SDMs predicted similar overlap in habitat suitability; however, mechanistic SDMs predicted habitat suitability to extend into regions without green salamanders but known to harbor many lungless salamanders. Under future warming scenarios, habitat suitability depended on climate scenario and SDM type. Correlative and hybrid models predicted a 42% reduction or 260% increase in area considered to be suitable depending on the climate scenario. In mechanistic SDMs, energetically suitable habitat declined with both climate scenarios and was driven by the thermal sensitivity of ri. Our study indicates that correlative‐only and hybrid approaches produce similar predictions of habitat suitability; however, discrepancies can arise for species that do not occupy their entire fundamental niche, which may hold consequences of conservation planning of threatened species.
... Nearly a millennium is required to grow limbs > 1 m diameter (Fig. 7c,d), and in Sequoia rainforests these often become colonized by the fern Polypodium scouleri (Sillett and Bailey, 2003), whose mats develop arboreal soils containing acidic residues that are extremely resistant to decomposition (Enloe et al., 2006(Enloe et al., , 2010. Layers of this material up to 1 m deep accumulate on limbs and in crotches between reiterated trunks, storing water and supporting considerable biodiversity ( Fig. 15c; Spickler et al., 2006;Sillett and Van Pelt, 2007). Large crowns of both redwoods contain enormous appendages (Sillett et al., 2015b), but substantially higher investment in heartwood defense (Fig. 4) may promote the extreme longevity that enables Sequoiadendron to retain appendages approaching or exceeding 2 m diameter even if all or part of them is dead (Figs. 8, 15d). ...
Article
Full-text available
The tallest conifers—Picea sitchensis, Pseudotsuga menziesii, Sequoia sempervirens, Sequoiadendron giganteum—are widely distributed in western North America, forming forests > 90 m tall with aboveground biomass ≥ 2000 Mg ha⁻¹. Here we combine intensive measurements of 169 trees with dendrochronology and allometry to examine tree and stand development. The species investing least in bark protection and heartwood defense—P. sitchensis—has more leaves, denser wood, larger appendages, and produces more aboveground biomass during its relatively brief lifespan than other conifers at equivalent ages. The species investing most in bark protection and heartwood defense—S. giganteum—has the least dense wood, largest appendages, and greatest longevity. Evidence for senescence diminishes with longevity; only P. sitchensis exhibits a post-maturity decline in tree productivity after accounting for leaf mass. Growth efficiency declines with age in all species, falling most rapidly in P. sitchensis followed by P. menziesii, S. sempervirens, and S. giganteum in the same sequence as longevity. Centuries-long time series of age, size, and growth increments identify years when trees first reach a given height as well as biomass and growth rates at that height, providing snapshots of performance useful for simulating development. Stands dominated by P. sitchensis and P. menziesii gain height at similar rates, but P. sitchensis accumulates biomass more rapidly until senescence curtails tree productivity, which takes centuries longer in P. menziesii. Whereas S. sempervirens in primary forest grows more slowly than P. sitchensis and P. menziesii until ~70 m tall, S. sempervirens in secondary forest outpaces other conifers with biomass increments approaching global maxima within a few centuries. Beyond ~70 m, S. giganteum gains height more slowly than other conifers, but it sustains relatively high biomass increments for millennia. Both within and beyond their native ranges, the four tallest conifers have unrealized potential to provide ecosystem services.
... Our encounter, however, is the first record of an aggregation of multiple N. brodiei individuals climbing a plant. Aggregation behavior in plethodontids is scarcely recorded, beyond breeding migrations or when resources become limited (Spickler et al., 2006;Petranka, 2010). The function of climbing behavior in plethodontid sala- manders is not well understood, but it may be to avoid predators, improve foraging, or to avoid competition with other salamanders (Jones et al., 2012;McEntire, 2016;Mezebish et al., 2018). ...
Article
The slender and elusive Nototriton brodiei is known only from a few specimens at two separate sites in the Sierra de Merendn, in Guatemala and Honduras. We present the first record of an aggregation of three adults of N. brodiei on a single leaf in the cloud forest of Cusuco National Park, Honduras. We observed two males and one female walking together at night, using one another as support to move across vegetation. This behavior is the first record of both sexes interacting for this species, and might represent courtship strategy or similar behavior. This observation is a contribution to the sparse natural history and ecology literature for this genus. Our observation highlights the need for herpetological research on little-known and imperiled species endemic to cloud forests in Central America.
... For example, in 1-ha of old-growth Sequoia sempervirens (coast redwood) forest, the 3 largest of 113 trees contain 30% of epiphyte mass, 54% of canopy soil, and 50% of arboreal water storage mostly on large limbs and crotches between reiterated trunks (Sillett and Van Pelt 2007). Living trees with decayed wood, large appendages, and scores of lichens and bryophytes provide refugia that sustains arboreal species, such as the wandering salamander and rare vascular plants, from one disturbance to the next (Spickler et al. 2006;Ishii et al. 2018;Gorman et al. 2019). Old-growth forests are widely recognized as important for charismatic species, including the endangered Northern Spotted Owl and Marbled Murrelet that depend on large limbs and broken-top trees for nesting (Hamer and Nelson 1995;LaHaye and Gutiérrez 1999). ...
Article
Full-text available
ContextWestern Olympic valley bottoms, disturbed by alluvial processes, are dominated by Picea sitchensis and isolated cohorts of Pseudotsuga menziesii, while upland contexts, disturbed by wind and fire, are dominated by P. menziesii. These forests have distinct structure and produce large trees with habitat for endangered birds.Objectives Describe how disturbance and forest development create landscape forest patterns and distribution of large trees in valley bottom and upland forests.Methods LiDAR data of ~ 9700 ha within Olympic National Park, USA was classified based on vegetation height and percent cover to contrast valley bottom and upland forests. Within-crown structure from 36 P. sitchensis and 12 P. menziesii was then used to predict locations of the largest and most complex trees.ResultsValley bottoms comprise small patches of dense tall (11%), medium-height trees (19%), and gaps (7%) embedded in open-canopy forest with scattered tall trees (63%). Upland forests comprise larger patches of tall (16%), medium (58%), and open-canopy forest (25%) with few gaps (1%). The largest trees are more abundant in valley bottoms (0.05 tree ha−1) than upland (0.02 tree ha−1) due to small patches of tall trees within open-canopy forest.Conclusions Alluvial disturbance, fungi-wind interaction, and dominance of late-successional fast-growing P. sitchensis create open-canopy forest with more large trees, while severe fire and wind interacting with P. menziesii create patchy closed-canopy forest with fewer large trees. Management for large habitat trees should use aggregated retention with P. menziesii, multi-aged selection techniques with P. sitchensis, and indefinitely retain a low density of large trees.
Article
Salamanders are often used as a model of early tetrapod locomotion, due to their generalized tetrapod body plan. We imaged five individuals of wandering salamander, Aneides vagrans, during horizontal and vertical locomotion and compared kinematic and gait adjustments made to compensate for each condition. We used ImageJ to calculate duty factor, stride length, stride frequency, contralateral foot spread, heading of climbing, and forward velocity. Like other terrestrial salamanders, A. vagrans use a diagonal couplet, lateral sequence walk on horizontal surfaces. When walking vertically, however, they use a single‐foot gait, taking smaller steps and extending the duty factor compared with level walking. Salamanders adjusted their limbs to have a wider contralateral foot spread between fore‐ and hindfeet when walking downward as compared to walking upward or horizontally. These gait adjustments may minimize the risk of slipping or falling by increasing the number of contact points during the stride cycle, and by bringing their center of mass closer to the surface. We found that salamanders moved at a significantly faster velocity when traveling horizontally compared to vertically. Furthermore, we found no significant difference between upward and downward velocity, despite greater stride lengths in upward locomotion; this was explained by a higher stride frequency in downward locomotion. We estimate travel time up or down an old‐growth redwood tree to be on the scale of hours, a significant time investment that may encourage alternatives when available. These results suggest that, in an ecological context, while salamanders are capable of traveling straight down a redwood tree, they may simply tend to jump. Studying the locomotion of plethodontid salamanders provides a window into how vertebrates with a generalized tetrapod body plan can adapt to a number of different landscapes. We imaged five individuals of wandering salamander, Aneides vagrans, during horizontal and vertical locomotion and compared kinematic and gait adjustments made to compensate for each condition. Salamanders adjusted their gait and exhibited lower stride length, higher duty factor, wider contralateral foot spread, and higher stride frequency when walking downwards. We estimate travel time for A. vagrans up or down old‐growth redwood trees, their natural habitat, to be on the scale of hours, suggesting that while these salamanders can walk straight down from tree habitats, jumping may be more feasible.
Article
Full-text available
Reviews the territorial behaviour of salamanders, with sections based on fundamental life history strategies: completely terrestrial; species that are terrestrial as adults but have complex life cycles (ie aquatic larvae); species with complex life cycles and predominantly semi-aquatic adults; and predominantly or completely aquatic species. After a brief discussion on salamander territoriality including sections on definitions and resource-area competition, frog territorality is covered, by way of comparison. -S.R.Harris
Article
Western red-backed salamander showed a high degree of site-specificity and maintained relatively small home ranges. Home ranges of adult males, adult females, and juveniles were similar in size (mean distance between the 2 farthest captures for adult males = 2.47 m, for adult females 1.71 m, for juveniles 1.95 m). Few cover objects, however, were used exclusively by a single adult as would be expected if the salamanders were territorial. Climatic conditions (cool and wet) in spring and autumn, when adults are active on the surface, are probably responsible for food (invertebrate prey) being readily available, thus rendering the defence of feeding territories uneconomical. -from Author
Article
This study of Aneides aeneus consisted of three parts, (1) determination and mapping of the distribution and habitat choice as revealed by the author's observations, literature and correspondence, (2) an investigation of the life history and ecology carried out intensively on two colonies in the vicinity of Highlands, North Carolina, and less intensively at four other localities in Georgia, North Carolina and South Carolina, (3) preliminary water loss tolerance tests in the laboratory. The distribution of Aneides aeneus coincides with the Appalachian Plateau and Blue Ridge physiographic provinces of Fenneman, there being no known occurrence of the species in the Appalachian Valley. In eastern Kentucky, southwestern Virginia and adjacent portions of Tennessee Aneides aeneus is found to occur in an arboreal or arboreal-rock crevice habitat. Its habitat in all other portions of its range is chiefly rock crevices. The region of arboreal habitat coincides with the undifferentiated mixed mesophytic forest of Braun, while the rock habitat generally occurs in regions of segregated forests of the mixed mesophytic type. Two areas, designated as (1) Highlands Study Area, and (2) South Satulah Area, were visited throughout a complete annual cycle and part of a second breeding season (April 30, 1949 to June 25, 1950). Rock crevices within these two areas were numbered and mapped. Fifty-two individual Aneides were marked by toe clipping and observations were made on the salamander population and on associated fauna and flora. During June, 1950, records were kept on temperature and humidity of the two localities. Data obtained on the crevices containing Aneides indicate two general types of crevice, one used for breeding, another used in a transitory manner. The crevices are moist but not wet, and are always shaded for the major portion of the day. Average daily maximum and minimum temperatures within the crevice were 5.3⚬ F. and 1.3⚬ F. respectively lower than those prevailing in the general area (within eight feet of the crevice) during the period June 8 to June 21, 1950. Relative humidity for the same period averaged 99.1 maximum and 75.3 minimum, with extremes of 100 and 61. This climatic picture is characteristic of the Highlands Plateau and adjacent montane areas. The annual cycle of Aneides aeneus was found to consist of four periods: (1) the breeding period, (2) the dispersal and aggregation period, (3) the hibernation period, (4) the post-hibernation aggregation and dispersal period. The breeding period, late May to late September, includes mating, egg laying and hatching. Egg laying was noted to have occurred prior to June 6 and to have been completed by June 14, 1949 on both study areas. In 1950, it was not completed by June 21 on either study area. Three females required 23, 27.5 and 30 hours to complete laying. The eggs typically form a cluster hanging from the ceiling of the crevice by several cables, but in some cases they are laid as a flattened mass. The color of the freshly laid eggs is whitishyellow and they have an average diameter of 4.5 mm. for the 62 eggs measured. The number of eggs varied from 10 to 26 (mean 17) per clutch in 22 clutches examined. The eggs are guarded by the female at all times, and the guarding period varies, depending on the activity of the newly hatched young. Intraoval development required an average of 86 days and 19 hours from laying to hatching (extremes 84 to 91 days) for five clutches observed. Twenty-eight newly hatched young from both study areas varied in total length from 18.5 to 23.0 mm. (mean 20.0) and in body length from 12.5 to 15 mm. (mean 13.1). The dispersal and aggregation period occurs from late September to November. The young and adult females leave the breeding crevices in most cases during this period. The young apparently choose moss filled crevices and ledges in which they are well concealed. The adults begin to gather in the vicinity of deep interconnecting crevices during October. It is believed that Aneides aeneus spends the winter in this type crevice. This assembling of individuals is spoken of as the pre-hibernation aggregation. Hibernation occurs from November through late April. On the evidence that individuals were more concentrated in deep anastomosing crevices, it is concluded that crevices of this type serve for hibernation purposes. No individuals were found beneath the soil surface or in rotten logs. Post-hibernation aggregation and dispersal occurs in late April and early May when the salamanders reappear and congregate in the vicinity of the "hibernation" crevices. Dispersal to the outlying breeding cervices takes place early in June. Where crevices are utilized for both breeding and "hibernation," Aneides may be sedentary. Since the greater portion of the non-hibernation cycle is spent by the female in egg laying and guarding of the young, they are naturally more sedentary than the male and immature salamanders. Both sexes are more active at night. Males generally remain in or near the crevices where first found, but marked individuals were noted to move as much as 300 feet. Changes in the visible population on the two study areas are shown graphically in figure 6. Fluctuations in the number of visible individuals and in their distribution throughout the areas are the result of difference in the activity of the organism during the four periods of the annual cycle. The fall peak is due to an influx of individuals around the "hibernation" crevices and is considered as the best time for censusing an Aneides population. Collecting at four localities revealed a significant departure from an expected one to one sex ratio when individuals obtained were tested by the chi-square method. This is believed to be due to selective collecting based on the habits of the species. Ptethodon jordani metaventris was frequently seen to occupy the larger and more easily accessible crevices, but rarely to occur in the same crevice with Aneides aeneus. Preliminary experiments comparing the two species with respect to vital limits of water loss were carried out in the laboratory. These indicate that A. aeneus is more capable physiologically to live in the relatively dry crevice habitat than is P. j. melaventris. Morphologically, the former is better adapted for climbing and entering very narrow crevices in the rock. It would seem that Aneides aeneus is able to escape direct competition with P. j. melayentris and other salamanders by selection of its ecologically peripheral niche, and this may be a factor in its continued survival over a large range. The sedentary nature of the species, plus the selection of a more or less specialized habitat, points to a colonial existence over its range, probably with little or no gene flow between colonies. Therefore, a study of geographic variation with this species should be made. Because of the similarity of the mixed mesophytic forest, in which Aneides aeneus is found to lead a semi-arboreal existence, to the transcontinental broad-leafed Tertiary forest (the Arcto-Tertiary Flora of Chaney, Condit and Axelrod), and since two of the western Aneides derived from a former transcontinental migrant are arboreal, the hypothesis that the arboreal habitat is primary and the rock habitat is secondary has been suggested.