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                  <text>The research in this publication was partially or fully funded by Colorado Parks and Wildlife.

Dan Prenzlow, Director, Colorado Parks and Wildlife • Parks and Wildlife Commission: Marvin McDaniel, Chair • Carrie Besnette Hauser, Vice-Chair
Marie Haskett, Secretary • Taishya Adams • Betsy Blecha • Charles Garcia • Dallas May • Duke Phillips, IV • Luke B. Schafer • James Jay Tutchton • Eden Vardy

�88

ARTICLE

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Latitudinal variation in snowshoe hare (Lepus americanus) body
mass: a test of Bergmann’s rule
Laura C. Gigliotti, Nathan D. Berg, Rudy Boonstra, Shawn M. Cleveland, Duane R. Diefenbach,
Eric M. Gese, Jacob S. Ivan, Knut Kielland, Charles J. Krebs, Alexander V. Kumar, L. Scott Mills,
Jonathan N. Pauli, H. Brian Underwood, Evan C. Wilson, and Michael J. Sheriff

Abstract: The relationship between body size and latitude has been the focus of dozens of studies across many species. However,
results of testing Bergmann’s rule — that organisms in colder climates or at higher latitudes possess larger body sizes — have
been inconsistent across studies. We investigated whether snowshoe hares (Lepus americanus Erxleben, 1777) follow Bergmann’s
rule by investigating differences in body mass using data from six published studies and from data of 755 individual hares
captured from 10 populations across North America covering 26° of north latitude. We also explored alternative hypotheses
related to variation in hare body mass, including winter severity, length of growing season, elevation, and snow depth. We found
body mass of hares varied throughout their range, but the drivers of body mass differed based on geographic location. In
northern populations, females followed Bergmann’s rule, whereas males did not. In northern populations, male mass was
related to mean snow depth. In contrast, in southern populations, body mass of both sexes was related to length of the growing
season. These differences likely represent variation in the drivers of selection. Speciﬁcally, in the north, a large body size is
beneﬁcial to conserve heat because of low winter temperatures, whereas in the south, it is likely due to increased food supply
associated with longer growing seasons.
Key words: snowshoe hare, Lepus americanus, latitudinal variation, energy expenditure, food supply, winter, snow depth, growing
season.
Résumé : Le lien entre la taille du corps et la latitude a fait l’objet de dizaines d’études portant sur de nombreuses espèces. Les
résultats des études visant à valider la règle de Bergmann, qui stipule que les organismes vivant en climat plus froid ou à plus
haute altitude auraient des corps de plus grandes tailles, ne sont pas cohérents d’une étude à l’autre. Nous avons vériﬁé si les
lièvres d’Amérique (Lepus americanus Erxleben, 1777) suivaient la règle de Bergmann en examinant les différences de masse
corporelle dans des données de six études publiées et pour 755 lièvres capturés de 10 populations réparties à la grandeur de
l’Amérique du Nord, sur un territoire couvrant 26° de latitude nord. Nous avons aussi examiné différentes hypothèses concernant les variations de la masse corporelle de lièvres, touchant notamment à la rigueur de l’hiver, la durée de la période
végétative, l’altitude et l’épaisseur de la neige. Nous avons constaté que la masse corporelle des lièvres varie dans toute leur aire
de répartition, mais que les facteurs qui l’inﬂuencent diffèrent selon l’endroit. Dans les populations nordiques, les femelles
suivent la règle de Bergmann, mais non les mâles. Dans les populations nordiques, la masse des mâles est reliée à l’épaisseur
moyenne de la neige, alors que dans les populations méridionales, la masse corporelle des deux sexes est reliée à la durée de la
période végétative. Ces différences représentent vraisemblablement des variations des facteurs inﬂuant sur la sélection. Plus
précisément, au nord, une grande taille du corps est utile parce qu’elle facilite la conservation de chaleur pour faire face aux

Received 23 July 2019. Accepted 4 September 2019.
L.C. Gigliotti. Department of Forestry and Environmental Conservation, Clemson University, 261 Lehotsky Hall, Clemson, SC 29634, USA.
N.D. Berg. U.S. Fish and Wildlife Service, National Wildlife Refuge System, Anchorage, AK 99503, USA.
R. Boonstra. Department of Biological Sciences, University of Toronto Scarborough, Toronto, ON M1C 1A4, Canada.
S.M. Cleveland. Department of Environmental and Forest Biology, State University of New York College of Environmental Science and Forestry,
Syracuse, NY 13210, USA.
D.R. Diefenbach. U.S. Geological Survey, Pennsylvania Cooperative Fish and Wildlife Research Unit, Pennsylvania State University, University Park,
PA 16802, USA.
E.M. Gese. U.S. Department of Agriculture, Wildlife Services, National Wildlife Research Center, Department of Wildland Resources, Utah State
University, Logan, UT 84322, USA.
J.S. Ivan. Colorado Parks and Wildlife, Fort Collins, CO 80526, USA.
K. Kielland. Department of Biology and Wildlife, Institute of Arctic Biology, University of Alaska Fairbanks, Fairbanks, AK 99775, USA.
C.J. Krebs. Department of Zoology, University of British Columbia, Vancouver, BC V6T 1Z4, Canada.
A.V. Kumar. Wildlife Biology Program, University of Montana, Missoula, MT 59812, USA.
L.S. Mills. Wildlife Biology Program, University of Montana, Missoula, MT 59812, USA; Ofﬁce of the Vice President for Research and Creative
Scholarship, University of Montana, Missoula, MT 59812, USA.
J.N. Pauli and E.C. Wilson. Department of Forest and Wildlife Ecology, University of Wisconsin-Madison, Madison, WI 53706, USA.
H.B. Underwood. U.S. Geological Survey, Patuxent Wildlife Research Center, Tunison Laboratory of Aquatic Science, Cortland, NY 13043, USA.
M.J. Sheriff. Biology Department, University of Massachusetts Dartmouth, Dartmouth, MA 02747, USA.
Corresponding author: Laura C. Gigliotti (email: lcgigli@clemson.edu).
Copyright remains with the author(s) or their institution(s). Permission for reuse (free in most cases) can be obtained from RightsLink.
Can. J. Zool. 98: 88–95 (2020) dx.doi.org/10.1139/cjz-2019-0184

Published at www.nrcresearchpress.com/cjz on 16 November 2019.

�Gigliotti et al.

89

faibles températures hivernales, alors que dans le sud, elle est probablement due à un meilleur approvisionnement en nourriture associé à des périodes végétatives plus longues. [Traduit par la Rédaction]
Mots-clés : lièvre d’Amérique, Lepus americanus, variation latitudinale, dépense énergétique, approvisionnement en nourriture,
hiver, épaisseur de la neige, période végétative.

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Introduction
Latitudinal variation in body size is a phenomenon common
across many taxa (McNab 1971; Ashton et al. 2000; Meiri and Dayan
2003). In particular, Bergmann’s rule states that, within a species
or clade, body mass is greater in cold climates, which leads to
latitudinal clines in body mass (Bergmann 1847). Individuals with
a larger body size possess a smaller surface area to volume ratio,
resulting in reduced rates of relative heat loss. This is advantageous for endotherms because it allows for survival at a lower
critical temperature (Brown et al. 2004). Bergmann’s rule has been
supported within geographically distinct populations of mammals, (e.g., packrats, genus Neotoma Say and Ord, 1825: Brown and
Lee 1969; elk, Cervus elaphus Linnaeus, 1758: Langvatn and Albon
1986; bobcat, Lynx rufus (Schreber, 1777): Wigginton and Dobson
1999) and birds (e.g., Singing Honeyeater, Meliphaga virescens
Vieillot, 1817 = Gavicalis virescens (Vieillot, 1817): Wooller et al. 1985;
Eurasian Sparrowhawk, Accipiter nisus (Linnaeus, 1758): Wyllie and
Newton 1994; Cerulean Warbler, Dendroica cerulea (A. Wilson,
1810) = Setophaga cerulea (A. Wilson, 1810): Jones et al. 2005). However, Bergmann’s rule has not been found in other species (e.g.,
coyote, Canis latrans Say, 1823: Thurber and Peterson 1991; Eurasian Blackcap, Sylvia atricapilla (Linnaeus, 1758): Telleria and
Carbonell 1999; brown bear, Ursus arctos Linnaeus, 1758: Kojola
and Laitala 2001). In a meta-analysis of birds and mammals, Meiri
and Dayan (2003) found that 72% of bird species and 65% of mammal species conformed to Bergmann’s rule.
However, factors that might be correlated with latitude, such as
food availability, may override the importance of heat conservation in driving within-species geographic body size variation
(Lindstedt and Boyce 1985; Millar and Hickling 1990). In New
World deer (Cervidae), Geist (1987) found the largest individuals
occurred in populations at middle latitudes where forage was
available for the longest time period, with smaller bodied individuals occurring at the highest and lowest latitudes. Similarly,
Erlinge (1987) found the European stoat or ermine (Mustela erminea
Linnaeus, 1758) exhibited body size variation in relation to prey
size and availability, rather than latitude. As such, patterns of
body size in relation to food availability are likely indirectly correlated with environmental factors such as length of growing
season, rainfall, or net primary productivity, which in turn inﬂuences forage and prey availability (McNab 2010; Huston and
Wolverton 2011). In addition, research has suggested animals with
larger surface area to volume ratios might not reduce heat loss as
expected, and larger animals might be at a disadvantage in cold
climates when resources are limited (McNab 1971), which has led to
some small mammals reducing their body size in winter (Dehnel’s
phenomena; Speakman 1996; Lovegrove 2005). Bergmann’s rule
has also been criticized for being overly simplistic, and only considering energetic costs of larger body sizes, while ignoring the
greater capacity for energy gains associated with larger size
(Speakman 1996). Support for Bergmann’s rule has been inconsistent and latitudinal gradients in body size may be driven by alternative mechanisms. However, understanding drivers of these
relationships is complicated by differences in measurement techniques across studies.
Snowshoe hares (Lepus americanus Erxleben, 1777) are an ideal
species to test Bergmann’s rule because they have a broad geographic range that spans both a latitudinal gradient from 36°N to
68°N and a broad temperature gradient. Additionally, they do not
hibernate and are nocturnal. Consequently, they experience the

coldest winter conditions. Previous research on morphometric
differences in snowshoe hare populations suggested that hares
were structurally larger in eastern North America, Alaska (USA),
and northwestern Canada, and smallest in the Paciﬁc Northwest
(Nagorsen 1985). However, as this previous study relied on cranial
measurements from shot or snared museum specimens, it was not
an ideal test of Bergmann’s rule because conformity to Bergmann’s
rule may be dependent on the size metric used (Meiri and Dayan
2003). We combine published body mass data from live-trapped
hares from 6 sites across their geographic range with raw capture
data from 10 sites (also from live-trapped hares) to assess whether
snowshoe hares conform to Bergman’s rule. As an alternative
hypothesis, we also tested whether snowshoe hare body mass may
be more strongly predicted by temperature (degree-days), length
of growing season, elevation, or snow depth.

Materials and methods
Published body mass data
Through a literature search using Google Scholar in April 2017
with terms “snowshoe hare” or “varying hare” and “body weight”
or “body mass” or “capture” or “trap”, we compiled winter body
mass data across the geographic range of snowshoe hares. We
limited our analysis to data collected on hares from December to
March to exclude bias from pregnant females, and we excluded
any studies in which male and female masses were pooled. Because postmortem treatment of carcasses could affect desiccation
and changes in body morphometrics, we excluded studies where
hares were shot or snared and not weighed immediately (including museum specimens). From this search, we used published
data from populations in Wyoming (USA) (Lawrence 1955), Oregon
(USA) (Black 1965), Idaho (USA) (Ellsworth et al. 2016), Manitoba
(Canada) (Murray 2002), British Colombia (Canada) (Sullivan and
Sullivan 1988), and the Yukon (Canada) (Trostel 1986).

®

Capture data
We compiled body mass data obtained on snowshoe hares captured across a range of latitudes from 10 different populations
(Fig. 1; Table 1). Study areas included San Juan Mountains, Colorado (USA); Taylor Park, Colorado (USA); Long Pond, Pennsylvania
(USA); Warren, Pennsylvania (USA); the southern portion of the
Bridger-Teton National Forest, Wyoming (USA); Wanakena, New
York (USA); Chequamegon National Forest, Medford District,
Wisconsin (USA); Seeley-Swan Valley, Montana (USA); the Kluane
region of the Yukon (Canada); and the Bonanza Creek Experimental Forest in Alaska (USA). Detailed descriptions of these study
areas can be found in Ivan et al. (2014) (Colorado); Gigliotti et al.
(2018) (Pennsylvania); Berg et al. (2012) (Wyoming); S.M. Cleveland,
unpublished data (New York); Wilson et al. (2019) (Wisconsin); Mills
et al. (2005) and Grifﬁn and Mills (2007) (Montana); Krebs et al.
(2001) (Yukon); and Kielland et al. (2010) (Alaska). For all populations, we trapped adult snowshoe hares during winter (December–
March) and recorded sex and body mass (using a Pesola spring
scale). If a hare was caught multiple times in a given season, then
we used measurements from only the ﬁrst capture. For hares
captured across multiple seasons, we averaged their initial capture mass across seasons. Capture and handling protocols were
approved by The Pennsylvania State University (No. 43476), The
University of Wisconsin-Madison (No. A005849), The University of
Montana (No. AUP 010-07), Environment Yukon (No. 202), The University of Alaska Fairbanks (No. 135211-5), The State University

®

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Can. J. Zool. Vol. 98, 2020

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Fig. 1. Location of snowshoe hare (Lepus americanus) populations used in analyses, including published measurements (triangles) and raw
capture data (circles), overlaid on the geographic range of the snowshoe hare (gray shading; NatureServe and IUCN 2012). Populations are
separated into northern contiguous populations (white symbols) and southern extension populations (black symbols). Population
abbreviations are found in Table 1.

of New York College of Environmental Science and Forestry
(No. 150401), Colorado State University and Colorado Parks and
Wildlife (No. 06-062A-03), and the U.S. Department of Agriculture,
National Wildlife Research Center (QA-491).
Environmental data
We calculated degree-days, length of growing season, and mean
daily snow depth (cm) for each study location (Table 1). We obtained daily minimum and maximum temperatures, as well as
daily snow depths, from the National Oceanic and Atmospheric
Administration’s National Climate Data Center (now known as
National Centers for Environmental Information; https://www.
ncdc.noaa.gov/). We selected the closest weather station (&lt;20 km)
to each of the study areas in our analyses. To ensure that years in
which each study was conducted was representative of the mean
weather conditions of the area, we used data starting 5 years prior
to the individual study period through the end of the data collection period. We calculated yearly degree-days for each location by
summing the daily minimum temperatures &lt;0 °C averaged across
years to obtain an overall degree-day value (Mills et al. 2013). We
calculated the length of the growing season for each location with
the climdex.pcic package for the program R (Bronaugh 2015),
which deﬁnes the growing season as the length of time between
the ﬁrst warm spell of the year (5 days with a mean temperature &gt;5 °C) and the ﬁrst cold spell of the year (5 days with a mean
temperature &lt;5 °C). We averaged the growing season length

across all years that data were collected for each study location.
We calculated elevation for each location using a 30 m digital
elevation model. We calculated mean daily snow depth for each
location by averaging the daily snow depth measurements across
all years of data collection. As a result, our snow depth metric can
be interpreted as an index of seasonality in that it incorporated
both the amount of snow during the winter and the number of
days that had snow.
Analysis
A test of Bergmann’s rule: body mass
For our analysis of Bergmann’s rule, we regressed body mass,
from both published literature and our capture-based data set,
with latitude. We ran models for males and females separately
because hares are known to exhibit sexual dimorphism (Whittaker and
Thomas 1983; Nagorsen 1985), and because of different energetics
between sexes (Ellsworth et al. 2016) resulting in different environmental factors inﬂuencing body size. Hare body mass and condition are associated with the phase of their population cycle,
with the greatest mass and condition occurring during the peak of
the cycle and the lowest mass and condition occurring during the
late low phase (Keith and Windberg 1978; Kielland et al. 2010). The
hare populations in the Yukon and Alaska exhibit 9- to 11-year
population cycles (Krebs et al. 1995; Kielland et al. 2010), whereas
those from Pennsylvania, New York, Wisconsin, Montana, Colorado,
Published by NRC Research Press

�Note: NA indicates that the study did not mention the cyclic phase or that the population is not known to cycle. N is the sample size. Researchers associated with the raw capture data are as follows: J.S. Ivan (J.S.I.),
L.C. Gigliotti (L.C.G.), D.R. Diefenbach (D.R.D.), N.D. Berg (N.D.B.), E.M. Gese (E.M.G.), S.M. Cleveland (S.M.C.), H.B. Underwood (H.B.U.), J.N. Pauli (J.N.P.), E.C. Wilson (E.C.W.), L.S. Mills (L.S.M.), R. Boonstra (R.B.), C.J. Krebs
(C.J.K.), M.J. Sheriff (M.J.S.), and K. Kielland (K.K.).

NA
NA
NA
NA
NA
NA
NA
NA
Late increase, peak
Late increase, peak
30.9
26.9
2.23
2.03
19.3
10.8
8.32
13.89
6.14
16.57
140
160
221
224
162
191
205
184
133
151
107
106.6
75
79
110
74
91
114
138
148
Colorado
Colorado
Pennsylvania
Pennsylvania
Wyoming
New York
Wisconsin
Montana
Yukon
Alaska
Raw capture data
J.S.I., this study
J.S.I., this study
L.C.G. and D.R.D., this study
L.C.G. and D.R.D., this study
N.D.B. and E.M.G., this study
S.M.C. and H.B.U., this study
J.N.P. and E.C.W., this study
L.S.M., this study
R.B., C.J.K., and M.J.S., this study
K.K., this study

CO1
CO2
PA1
PA2
WY1
NY
WI
MT
YT1
AK

38
38.8
41
41.7
43
44
45
47
60
64

3429
2903
580
566
2877
571
454
1225
781
136

–2654.26
–2992.1
–939.8
–910.5
–2058.7
–1776.8
–1851.2
–1480.8
–3366.1
–4067.5

12
53
38
22
599
131
NA
NA
NA
Low
Late increase, peak, decline
NA
1.03
0.05
12.32
3.03
8.62
5.98
164
305
143
172
187
124
106
122
116
98
122
138
Wyoming
Oregon
Idaho
Manitoba
British Columbia
Yukon
Published data
Lawrence 1955
Black 1965
Ellsworth et al. 2016
Murray 2002
Sullivan and Sullivan 1988
Trostel 1986

WY2
OR
ID
MB
BC
YT2

Location
Study citation

Abbreviation

41
44
48
51
53
61

2640
869
825
280
960
817

–1635.4
–152.22
–1054.5
–2754.9
–1665.2
–4334.4

N
Cyclic phase
Mean daily
snow depth
(cm)
Longitude
(°W)

Elevation
(m)

Degree-days
(°C)

Growing
season
(days)

118
189
48
12
91
6
45
79
122
45

91

Latitude
(°N)

Table 1. Summary of studies reporting snowshoe hare (Lepus americanus) body mass data used in our analyses.

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Gigliotti et al.

Table 2. Model selection results for regressions of drivers of snowshoe hare (Lepus americanus) winter body mass.
Sex

Model

⌬AICc

–2 × ln(L)

Model
likelihood

w

k

Female

Elevation
Snow depth
Intercept only
Latitude
Growing season
Degree-days
Elevation
Intercept only
Snow depth
Latitude
Growing season
Degree-days

0.00
1.03
2.45
3.26
4.06
4.40
0.00
0.69
1.24
2.28
2.29
2.67

209.25
210.25
213.72
212.53
213.33
213.61
212.35
215.04
213.60
214.63
214.64
215.02

1.00
0.60
0.29
0.19
0.13
0.11
1.00
0.71
0.54
0.32
0.32
0.26

0.43
0.26
0.12
0.08
0.06
0.05
0.32
0.22
0.17
0.10
0.10
0.08

2
2
1
2
2
2
2
1
2
2
2
2

Male

Note: All locations were included, with data from Alaska and Yukon populations being restricted to hares measured during the high phases of the 10-year
population cycle. AICc is Akaike’s information criterion corrected for small
sample size; –2 × ln(L) is log-likelihood, where L is likelihood; w is Akaike model
weight; k is the number of model parameters.

and Wyoming are non-cyclic or weakly cyclic (Keith et al. 1993;
Hodges 2000; Murray 2000). Because we expected patterns conforming to Bergmann’s rule to be most apparent during the times
which hares are the largest, we ran models with data from the
ﬁnal year of the increase phase and peak year for the Yukon (2006)
and Alaska (1999, 2008–2009). We were not able to standardize
cyclic phase for data from the published literature.
We speciﬁed six a priori regression models to explore the relationship between snowshoe hare body mass and latitude, as well
as alternative drivers of body mass. We considered a linear latitude model, a degree-day model, a growing season model, an elevation model, a snow depth model, and an intercept-only model.
We ran all analyses using the lm function in the program R (R Core
Team 2019). We compared models using Akaike’s information
criterion corrected for small sample size (AICc) (Burnham and
Anderson 2002) and considered models within 2 AICc units of the
top model to be competitive.
Locational differences in hare morphometrics
Because populations that project beyond the contiguous range
of a species may encounter signiﬁcantly different environmental
forces, we also assessed the conformity to Bergmann’s rule on
geographic subsets of our data. Speciﬁcally, we separated out the
populations into a contiguous northern group, demarcated by
unbroken segments in the range map of the species (Fig. 1), and a
southern extension group, demarcated by projecting segments in
the range map of the species (Fig. 1). Based on this classiﬁcation,
we included Alaska, Yukon, British Columbia, Manitoba, and
Wisconsin populations in the contiguous northern analysis, and
Pennsylvania, New York, Colorado, Wyoming, Montana, Idaho,
and Oregon populations in the southern extension analysis. These
southern populations mostly coincide with southern projections
along mountain ranges.
We also conducted our analysis of the southern populations
without the Oregon population because this population, like
other populations in the Cascades, experience reduced seasonality, mild winters, and live in areas that were historical glacial
refugia (Nagorsen 1985; Cheng et al. 2014). The historic and current environmental conditions that these populations encounter
differ from the other populations in our analysis; therefore, evolutionary forces acting upon this population may have resulted in
selection for different characteristics. Hare populations in the
Cascades have high genetic uniqueness compared with other hare
populations (Cheng et al. 2014).
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Fig. 2. Relationship between snowshoe hare (Lepus americanus) winter body mass and latitude for females (solid circles) and males (open
squares) using published and raw capture body mass data. Locations are labeled using abbreviations found in Table 1 and represent high
cyclic phases of Yukon and Alaska populations.

Table 3. Model selection results for regressions of drivers of snowshoe hare (Lepus americanus) winter body mass for northern contiguous
populations, using data from high phases of the Alaska and Yukon
populations.
Sex

Model

⌬AICc

–2 × ln(L)

Model
likelihood

w

k

Female

Latitude
Snow depth
Degree-days
Growing season
Intercept only
Elevation
Snow depth
Latitude
Intercept only
Degree-days
Growing season
Elevation

0.00
1.30
2.69
4.30
4.53
6.25
0.00
7.23
7.24
8.54
9.00
9.06

68.60
69.90
71.29
72.90
75.13
74.85
67.06
74.29
76.30
75.61
76.07
76.12

1.00
0.52
0.26
0.12
0.10
0.04
1.00
0.03
0.03
0.01
0.01
0.01

0.49
0.25
0.13
0.06
0.05
0.02
0.92
0.02
0.02
0.01
0.01
0.01

2
2
2
2
1
2
2
2
1
2
2
2

Male

Note: AICc is Akaike’s information criterion corrected for small sample size;
–2 × ln(L) is log-likelihood, where L is likelihood; w is Akaike model weight; k is
the number of model parameters.

Results
A test of Bergmann’s rule: body mass
Across all populations, hare winter body mass was not associated with latitude, and therefore did not follow Bergmann’s rule
(Table 2; Fig. 2). For females, the mean winter body mass (g) was
best described by elevation or mean snow depth (Table 2). Female
snowshoe hares were larger at lower elevations and in locations
with shallower snow depths. For every 10 m increase in elevation,
the body mass of females decreased by 0.87 g, and for every 1 cm
increase in snow depth, the body mass of females decreased by 9 g.
For males, the mean winter body mass was best described by
elevation or mean snow depth, but the 85% conﬁdence intervals of
the snow depth parameter overlapped zero indicating that it was

Fig. 3. Relationship between female snowshoe hare (Lepus americanus)
winter body mass and latitude for northern contiguous populations.

uninformative (␤ = –6.25; 85% CI = –14.57 to 2.02). Male snowshoe
hares were larger at lower elevations, and for every 10 m increase
in elevation, the body mass of males decreased by 0.72 g.
Northern contiguous populations
The mean body mass of females in the northern contiguous
region was best described by latitude or mean snow depth
(Table 3). Based on the latitude model, females in the northern
contiguous region followed Bergmann’s rule, with body mass increasing 13.3 g for every 1° increase in latitude (Fig. 3). Based on the
snow depth model, female snowshoe hare body mass was positively associated with snow depth, with body mass increasing
19.5 g with each 1 cm increase in mean snow depth (Fig. 4). The
mean body mass of males in the northern contiguous region was
best described by mean snow depth (Table 3). Based on this model,
male body mass was positively associated with mean snow depth,
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Fig. 4. Relationship between female snowshoe hare (Lepus americanus)
winter body mass and mean snow depth for northern contiguous
populations.

93

Table 4. Model selection results for regressions of drivers of snowshoe hare (Lepus americanus) winter body mass for southern extension
populations.
Sex

Model

⌬AICc

–2 × ln(L)

Model
likelihood

w

k

Female

Growing season
Snow depth
Elevation
Degree-days
Intercept only
Latitude
Growing season
Snow depth
Elevation
Intercept only
Degree-days
Latitude

0.00
8.00
9.73
9.85
11.68
13.59
0.00
6.24
6.84
7.74
8.07
9.61

110.69
118.67
120.42
120.54
124.37
124.27
115.25
121.49
122.10
124.99
123.33
124.86

1.00
0.02
0.01
0.01
0.00
0.00
1.00
0.04
0.03
0.02
0.02
0.01

0.96
0.02
0.01
0.01
0.00
0.00
0.89
0.04
0.03
0.02
0.01
0.01

2
2
2
2
1
2
2
2
2
1
2
2

Male

Fig. 5. Relationship between male snowshoe hare (Lepus americanus)
winter body mass and mean snow depth for northern contiguous
populations.

Note: AICc is Akaike’s information criterion corrected for small sample size;
–2 × ln(L) is log-likelihood, where L is likelihood; w is Akaike model weight; k is
the number of model parameters.

Fig. 6. Relationship between snowshoe hare (Lepus americanus)
winter body mass and growing season length for females (solid
circles and solid line) and males (open squares and broken line) for
southern extension populations.

with body mass increasing 24.9 g with each 1 cm increase in mean
snow depth (Fig. 5).
Southern extension populations
The mean winter body mass of both females and males in the
southern extension region was best described by length of the
growing season (Table 4). Based on this model, both female and
male body mass was positively associated with growing season
length, with body mass increasing 6.6 and 6.3 g, respectively, with
each 1-day increase in growing season length (Fig. 6).

Discussion
Body mass of snowshoe hares only conformed to Bergmann’s
rule in certain portions of their range. Speciﬁcally, females in
northern contiguous populations followed Bergmann’s rule (Fig. 3)
and also body mass increased with snow depth, whereas body
mass of males in northern contiguous populations was only positively related to mean snow depth (Fig. 4). In the southern
extension populations, the body mass of female and male hares
increased with length of the growing season (Fig. 5).
In northern contiguous populations, the conformity of females
to Bergmann’s rule can be explained by the harsh winters experienced by the northernmost populations. Maintaining a greater
body mass is likely beneﬁcial for two reasons: reduced relative
heat loss because of a smaller surface area to volume ratio (James
1970) and enhanced fasting endurance (Lindstedt and Boyce 1985;
Millar and Hickling 1990). Bergmann’s rule was formulated based
on the heat retention hypothesis and larger body masses have
been found to be associated with increased absolute heat production and higher cooling resistance in a variety of species

(Scholander et al. 1950; Gillooly et al. 2001). In addition to other
adaptations, such as lower metabolic rates and increased winter
pelage insulation (Sheriff et al. 2009), a larger body mass potentially helps hares in the coldest parts of their range maintain a
proper heat balance in winter. A relatively greater body mass also
may enhance the ability of hares in the north to cope with a long
winter of poor food availability by increasing their energy reserves. For example, moose (Alces alces (Linnaeus, 1758)) in Sweden
have been found to follow Bergmann’s rule in regard to body
mass; this relationship is likely driven by fat reserves that help
them survive the winter (Sand et al. 1995). However, we do not
believe that this is the case with hares, as they have little if any fat
accumulation in winter (Hodges et al. 2006) and cannot survive for
more than a day without eating (Pease et al. 1979; Whittaker and
Thomas 1983). Thus, we suggest that the greater body mass of
female hares in the most northern populations is to reduce heat
loss (sensu stricto Bergman’s rule; Bergmann 1847).
We did not see the same relationship between body mass and
latitude for male hares in the northern contiguous populations.
This lack of support for Bergmann’s rule for males might be a
consequence of different energy demands of males compared
with females (Ellsworth et al. 2016). In most mammalian species,
females have higher energetic demands than males because of the
large energetic requirements associated with gestation and lactation (Gittleman and Thompson 1988). Because snowshoe hares
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94

breed in the late-winter months when temperatures are still low,
maintaining a high winter body mass might be the most essential
for female hares in populations that experience the highest thermal energy demands.
The body mass of males in the northern contiguous populations
was positively related to snow depth. Higher body masses could be
disadvantageous for hares in areas of deep snow because of increased foot-loading and associated energetic costs (Murray and
Boutin 1991; Crête and Larivière 2003). However, as snow accumulates, hares have access to more vegetation during the winter
because they are able to access taller shrubs and vegetation
(Meslow and Keith 1971), which in turn could reduce overwinter
mass loss and result in higher body masses in winter. In addition,
males in northern populations with higher body masses may also
have larger feet, which would reduce foot-loading and minimize
the negative effects of larger body masses in areas with deeper
snow. Females in northern contiguous populations might not follow the same pattern of higher body masses with deeper snow
because their body mass might be more driven by reproductive
energetic demands. Finally, because we calculated mean snow
depth across the entire year, higher mean snow depths are also
associated with longer time periods with snow on the ground, and
thus lower winter food availability. As a result, it would be beneﬁcial for hares in areas with more snow to have larger body
masses to survive during longer times of reduced food availability
(Hodges et al. 2006).
In the southern extension populations, hare body mass was
related to the length of the growing season. Many of these southern populations experience milder winter conditions; therefore,
heat conservation may not be as important of a driver of body
mass as it is for more northern populations (Gigliotti et al. 2017).
Hares in areas with longer growing seasons have more opportunity to gain mass over the summer, which in turn could result in
higher body masses in winter (Lindstedt and Boyce 1985). Furthermore, they have less time to lose mass over the winter, given its
shorter duration. Food availability has also been shown to drive
latitudinal relationships with body size in other taxa (Geist 1987;
Wolverton et al. 2009).
Our results are similar to those of Nagorsen (1985), who found
that hares in eastern North America, Alaska, and northeastern
Canada had larger cranial measurements than hares in other regions. Additional, in both studies, hares were smallest, either in
cranial measurements or body mass, in the Paciﬁc Northwest. The
similarity of our results indicates that body mass and cranial measurements are likely correlated and that the same general patterns between size and latitude can be found regardless of the size
metric used.
Conclusions
Body mass of snowshoe hares varies across their distributional
range, but they only conform to Bergman’s rule in the central and
northern extent of the range of the species. In contrast, the body
mass of hares in southern extension populations is driven by the
length of the growing season. Thus, the selective forces driving
these patterns vary: in the north, the size and mass of hares may
be driven by their need to conserve heat and energy during a long
and cold winter; whereas in the south, the size and mass of hares
may be driven by increased food availability. For species that have
extensive geographic ranges, such as snowshoe hares, it appears
important to understand local factors that govern site-speciﬁc
adaptations, rather than attempting to ﬁt an all-encompassing
general taxonomic explanation.

Acknowledgements
We thank the anonymous reviewers who made comments that
improved the manuscript. Any use of trade, ﬁrm, or product
names is for descriptive purposes only and does not imply endorsement by the U.S. Government.

Can. J. Zool. Vol. 98, 2020

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              <text>The relationship between body size and latitude has been the focus of dozens of studies across many species. However, results of testing Bergmann’s rule — that organisms in colder climates or at higher latitudes possess larger body sizes — have been inconsistent across studies. We investigated whether snowshoe hares (Lepus americanus Erxleben, 1777) follow Bergmann’s rule by investigating differences in body mass using data from six published studies and from data of 755 individual hares captured from 10 populations across North America covering 26° of north latitude. We also explored alternative hypotheses related to variation in hare body mass, including winter severity, length of growing season, elevation, and snow depth. We found body mass of hares varied throughout their range, but the drivers of body mass differed based on geographic location. In northern populations, females followed Bergmann’s rule, whereas males did not. In northern populations, male mass was related to mean snow depth. In contrast, in southern populations, body mass of both sexes was related to length of the growing season. These differences likely represent variation in the drivers of selection. Specifically, in the north, a large body size is beneficial to conserve heat because of low winter temperatures, whereas in the south, it is likely due to increased food supply associated with longer growing seasons.&lt;br /&gt;&lt;br /&gt;Le lien entre la taille du corps et la latitude a fait l’objet de dizaines d’études portant sur de nombreuses espèces. Les résultats des études visant à valider la règle de Bergmann, qui stipule que les organismes vivant en climat plus froid ou à plus haute altitude auraient des corps de plus grandes tailles, ne sont pas cohérents d’une étude à l’autre. Nous avons vérifié si les lièvres d’Amérique (Lepus americanus Erxleben, 1777) suivaient la règle de Bergmann en examinant les différences de masse corporelle dans des données de six études publiées et pour 755 lièvres capturés de 10 populations réparties à la grandeur de l’Amérique du Nord, sur un territoire couvrant 26° de latitude nord. Nous avons aussi examiné différentes hypothèses concernant les variations de la masse corporelle de lièvres, touchant notamment à la rigueur de l’hiver, la durée de la période végétative, l’altitude et l’épaisseur de la neige. Nous avons constaté que la masse corporelle des lièvres varie dans toute leur aire de répartition, mais que les facteurs qui l’influencent diffèrent selon l’endroit. Dans les populations nordiques, les femelles suivent la règle de Bergmann, mais non les mâles. Dans les populations nordiques, la masse des mâles est reliée à l’épaisseur moyenne de la neige, alors que dans les populations méridionales, la masse corporelle des deux sexes est reliée à la durée de la période végétative. Ces différences représentent vraisemblablement des variations des facteurs influant sur la sélection. Plus précisément, au nord, une grande taille du corps est utile parce qu’elle facilite la conservation de chaleur pour faire face aux faibles températures hivernales, alors que dans le sud, elle est probablement due à un meilleur approvisionnement en nourriture associé à des périodes végétatives plus longues. [Traduit par la Rédaction]</text>
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          <name>Bibliographic Citation</name>
          <description>A bibliographic reference for the resource. Recommended practice is to include sufficient bibliographic detail to identify the resource as unambiguously as possible.</description>
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            <elementText elementTextId="4128">
              <text>Gigliotti, L. C., N. D. Berg, R. Boonstra, S. M. Cleveland, D. R. Diefenbach, E. M. Gese, J. S. Ivan, K. Kielland, C. J. Krebs, A. V. Kumar, L. S. Mills, J. N. Pauli, H. B. Underwood, E. C. Wilson, and M. J. Sheriff. 2019. Latitudinal variation in snowshoe hare (&lt;em&gt;Lepus americanus&lt;/em&gt;) body mass: a test of Bergmann’s rule. Canadian Journal of Zoology 98:88–95. &lt;a href="https://doi.org/10.1139/cjz-2019-0184" target="_blank" rel="noreferrer noopener"&gt;https://doi.org/10.1139/cjz-2019-0184&lt;/a&gt;</text>
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        <element elementId="39">
          <name>Creator</name>
          <description>An entity primarily responsible for making the resource</description>
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            <elementText elementTextId="4129">
              <text>Gigliotti, Laura C.</text>
            </elementText>
            <elementText elementTextId="4130">
              <text>Berg, Nathan D.</text>
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            <elementText elementTextId="4131">
              <text>Boonstra, Rudy</text>
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            <elementText elementTextId="4132">
              <text>Cleveland, Shawn M.</text>
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            <elementText elementTextId="4133">
              <text>Diefenbach, Duane R.</text>
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            <elementText elementTextId="4134">
              <text>Gese, Eric M.</text>
            </elementText>
            <elementText elementTextId="4135">
              <text>Ivan, Jacob S.</text>
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            <elementText elementTextId="4136">
              <text>Kielland, Knut</text>
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              <text>Krebs, Charles J.</text>
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              <text>Kumar, Alexander V.</text>
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              <text>Mills, L. Scott</text>
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              <text>Pauli, Jonathan N.</text>
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              <text>Underwood, H. Brian</text>
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              <text>Wilson, Evan C.</text>
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            <elementText elementTextId="4143">
              <text>Sheriff, Michael J.</text>
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        <element elementId="49">
          <name>Subject</name>
          <description>The topic of the resource</description>
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              <text>Snowshoe hare</text>
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              <text>&lt;em&gt;Lepus americanus&lt;/em&gt;</text>
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              <text>Latitudinal variation</text>
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              <text>Energy expenditure</text>
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              <text>Food supply</text>
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              <text>Winter</text>
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              <text>Snow depth</text>
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              <text>Growing season</text>
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          <name>Extent</name>
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            <elementText elementTextId="4152">
              <text>8 pages</text>
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          <name>Date Created</name>
          <description>Date of creation of the resource.</description>
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            <elementText elementTextId="4153">
              <text>2019-11-16</text>
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          <name>Rights</name>
          <description>Information about rights held in and over the resource</description>
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            <elementText elementTextId="4154">
              <text>&lt;a href="http://rightsstatements.org/vocab/InC-NC/1.0/" target="_blank" rel="noreferrer noopener"&gt;In Copyright - Non-Commercial Use Permitted&lt;/a&gt;</text>
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          <name>Format</name>
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            <elementText elementTextId="4156">
              <text>application/pdf</text>
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          <name>Language</name>
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            <elementText elementTextId="4157">
              <text>English; French (Abstract only)</text>
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          <name>Is Part Of</name>
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              <text>Canadian Journal of Zoology</text>
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