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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

�Does a Population of Cougars Exist in Michigan?
Authors: Kurta, Allen, SCHWARTZ, MICHAEL K., and ANDERSON,
CHARLES R.
Source: The American Midland Naturalist, 158(2) : 467-471
Published By: University of Notre Dame
URL: https://doi.org/10.1674/00030031(2007)158[467:DAPOCE]2.0.CO;2

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�Am. Midl. Nat. 158:467–471

Does a Population of Cougars Exist in Michigan?
ABSTRACT.—After analyzing DNA obtained from fecal samples gathered in Michigan,
Swanson and Rusz (2006) claimed that 83% of identified scats were from cougars, indicating
to them that a population of these large carnivores existed in the state. In this paper, we
identify problems with their methodology, suggest that they unreasonably extrapolated their
conclusions and point out that their results are improbable, especially in light of no other
evidence in the scientific literature suggesting the existence of a population of cougars in
Michigan.
INTRODUCTION
The cougar (Puma concolor) historically was the most widely distributed terrestrial mammal in the New
World, other than humans (Biek et al., 2006). During the late 19th and early 20th centuries, North
American populations of cougars declined substantially due to human persecution, habitat loss and
depletion of prey, especially wild ungulates (Culver et al., 2000; Logan and Sweanor, 2001; Biek et al.,
2006). The species became extinct throughout most of the East, although this large felid continued to
live in many parts of the West. Since the 1970s, western populations appeared to have increased in size
(Logan and Sweanor, 2000; Biek et al., 2006) and recolonization of some historically occupied regions
has occurred (Novak et al., 1987; Linnell et al., 2001).
In Michigan, most biologists believed that the cougar was extirpated from the Lower Peninsula by
1875 and from the more rugged Upper Peninsula by the early 1900s (Baker, 1983; Kurta, 1995).
Nevertheless, there has been a long history of unsubstantiated reports of cougars in the state (Baker,
1983; R. H. Baker, in litt.), with many accounts appearing in the popular media during the last 10–15 y,
suggesting to some people that this felid may be recolonizing Michigan or that a persistent relict
population exists (Belant et al., 2006). Recently, Swanson and Rusz (2006) published what they believed
was strong physical evidence, based on DNA obtained from fecal samples, for a population of at least
eight cougars in Michigan between 2001 and 2003. The subspecies of cougar that originally was found in
Michigan (Puma concolor couguar) is on the federal list of endangered species, and presence of
a population of these animals would have profound management implications for state and federal
agencies and how they spend limited conservation resources. More importantly, the claims of Swanson
and Rusz have contributed to highly publicized fears for public safety (e.g., Donnelly, 2007). Herein, we
describe several concerns that we have regarding the methodology and conclusions of Swanson and
Rusz (2006) and address the improbability of their results.
CRITIQUE
Problems with genetic methodologies.—Swanson and Rusz (2006) identify species from scat using
a modification of a method published by Foran et al. (1997). This method attempts to examine
a segment of DNA that is quite large (ca. 700 base pairs). Unfortunately, large segments of DNA from
noninvasive genetic samples, such as scat, rarely are amplified accurately because of the high level of
degradation typically associated with these types of samples (Mills et al., 2000). The method of Foran et
al. (1997) also relies on a region of the genome that contains an 80-bp tandem repeat unit (Lopez et al.,
1996; Foran et al., 1997). Mills et al. (2000), in contrast, describe a newer method for identifying
carnivores that examines a much shorter segment of DNA (ca. 360 base pairs) and uses the 16s rRNA
region, a section of the genome without the 80-bp tandem repeat. In fact, the motivation behind
developing the 16s-rRNA test in Mills et al. (2000) was failure of the method of Foran et al. (1997) to
produce consistent results. In the Wildlife Genetics Laboratory of USDA Forest Service, Rocky Mountain
Research Station, amplification of DNA from the large region of the genome containing the tandem
repeat unit (i.e., the method of Foran et al., 1997) has a low rate of success and potentially yields
misleading results, possibly because the number of repeat units varies in different individuals of the
same species (K. Pilgrim, pers. comm.). Reliance on the method of Foran et al. (1997) likely explains the
low success rate (4%) that Swanson and Rusz (2006) report for amplifying DNA from fecal samples.

467
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Furthermore, Swanson and Rusz (2006) do not properly apply the approach of Foran et al. (1997).
The first step in the technique of Foran et al. (1997) is to amplify DNA, and the second step is to cut the
DNA with diagnostic restriction enzymes, which is the same approach used by Mills et al. (2000). Both
methods also require a panel of multiple restriction enzymes to produce diagnostic results for felids.
The technique of Foran et al. (1997) requires use of two restriction enzymes to distinguish among the
four felids found in the northern United States: bobcat (Lynx rufus), Canada lynx (L. canadensis),
cougar and domestic cat (Felis catus). Swanson and Rusz (2006), however, only used one restriction
enzyme (RsaI). Although the original primers used by Foran et al. (1997) would distinguish bobcat from
cougar based on RsaI, they would fail to distinguish cougar from lynx (Foran et al., 1997:837–838). To
distinguish lynx from cougar, Swanson and Rusz (2006) should have used the restriction enzyme HinfI.
Note the absence of a sample from lynx as a control in figure 2 of Swanson and Rusz (2006).
It is possible, but unlikely, that the modified primers used by Swanson and Rusz (2006) could separate
lynx from cougars, but this never was demonstrated. The authors may have assumed that lynx do not
exist in the area or that scat from lynx and cougar can be identified reliably using morphology; if so,
they are incorrect. Although lynx are rare in Michigan, there are many verified records of lynx in the
Upper Peninsula since the early 1900s (Harger, 1965; Baker, 1983; McKelvey et al., 2000; Beyer et al.,
2001), with a confirmed lynx collected by a trapper in the Hiawatha National Forest in 2003
(S. Mighton, pers. comm.). We also question whether it is possible to distinguish reliably scats of lynx
from those of cougar based on morphology because suspected cougar scats sent to the Wildlife Genetics
Laboratory often are determined to be those of lynx based on either sequencing of DNA or the
restriction-digest test of Mills et al. (2000; K. Pilgrim, pers. comm.).
We have two other concerns regarding images of gels presented by Swanson and Rusz (2006). First, in
theory, the method of Foran et al. (1997), when applied properly, differentiates domestic cats from
cougars based on examining the RsaI restriction digest. However, we have found, in practice, that unless
positive standards (‘‘knowns’’) for domestic cat and cougar are run simultaneously on a gel, it would be
difficult to distinguish these species. Nevertheless, Swanson and Rusz (2006) only used standards from
‘‘three known bobcats, cougars, wolves, and coyotes’’ and not domestic cats. Second, RsaI-restricted
samples from bobcats produce only a single band (Foran et al.,1997), yet figure 2b in Swanson and Rusz
(2006) clearly shows two lower bands in the same size range as those of cougar. These extra lower bands
for the bobcat have various possible causes, including contamination, but their unexplained presence in
the gels of Swanson and Rusz (2006) is troubling.
Extrapolating beyond supported results.—Swanson and Rusz (2006:370) claim positive identification of
cougars from 10 samples gathered at eight sites, and conclude that there were ‘‘at least eight [cougars]
in Michigan over the 3 y of this study.’’ They base this statement on the fact that the eight sites were
separated by at least 56 km and the assumption that it was unlikely, given limited searching for scats in
the field, that ‘‘we could have found scat dropped by the same cougar (dispersing or resident) at any
two locations’’ (Swanson and Rusz, 2006:369). However, size of home range for male cougars typically is
200–500 km2, with some ranges as large as 792 km2 (Logan and Sweanor, 2000). In addition, young
cougars dispersing from their natal home often travel more than 100 km, and distances over 1000 km
have been documented (Logan and Sweanor, 2000, 2001; Thompson and Jenks, 2005). Furthermore,
samples that Swanson and Rusz (2006) identified as cougar in Michigan were obtained over 3 y. We
contend that distance between samples cannot be used reliably to infer separate identity and minimum
number alive, given the time over which the samples were collected and the documented ability of
cougars to move hundreds of kilometers. In addition, Swanson and Rusz (2006:369) refer to these eight
putative cougars as the ‘‘Michigan population,’’ but there is no evidence that these animals, if they were
cougars, were part of a resident population, as opposed to individuals dispersing from other states or
recently released captives.
There are well-established molecular methods (e.g., analysis of microsatellites) that can determine
individual identity from scats produced by cougars (e.g., Ernest et al., 2000; Sinclair et al., 2001; Anderson
et al., 2004; McRae et al., 2005; Biek et al., 2006). If Swanson and Rusz (2006) had run microsatellites on
their 10 positive scats, then they could have made some inferences as to the minimum number of
cougars alive in Michigan. In addition, some of these microsatellites produce allele lengths in
a distribution that is species-specific in parts of the cougar’s geographic range (see fig. 2 in Ernest et al.,

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NOTES AND DISCUSSION

469

2000). Thus, using microsatellites could have confirmed the identity of species that Swanson and Rusz
(2006) obtained from mitochondrial DNA. Lastly, there are felid-specific tests to determine gender that
have been designed for use with scats and hairs (Pilgrim et al., 2005), and these tests could have been
used to determine if both males and females were present in the ‘‘population.’’ Overall, without
employing such tests and the previously mentioned problems with the methodology that they did use,
a more cautious interpretation of the data is warranted.
Improbable results.—Swanson and Rusz (2006) succeeded in amplifying DNA from 12 of 297 scats (4%
of samples examined), with 10 samples attributed to cougars (83% of identified samples), one to
bobcat, and one to a canid. The rate of success for amplifying DNA likely would have been much higher
had they employed methods outlined in Mills et al. (2000). If Swanson and Rusz (2006) obtained
identifications for 90% of their 297 scats (a rate achieved by McKelvey et al., 2006 in another study of
wild felids) and 83% were cougars, Swanson and Rusz (2006) would have identified 223 samples as
cougar. The high proportion of cougars among the samples identified by Swanson and Rusz (2006) and
the absolute number of cougars that presumably would result if more samples actually had yielded
amplified DNA seem improbable—especially without any supporting evidence in the scientific literature
that a population occurs in the state.
Cougars often are killed by trains, trucks or automobiles (Logan and Sweanor, 2000; Heist et al.,
2001), but there is no report in the scientific literature that such a deadly collision ever has occurred in
Michigan. Hunting is a significant cause of mortality for cougars, even in states where they are protected
(Logan and Sweanor, 2000), yet there is no verifiable record of a cougar being shot in Michigan since
the early 1900s (Baker, 1983). Similarly, cougars are caught inadvertently in traps set for other types of
mammals (e.g., Wyoming Game and Fish Department, 2006), but there is no record of this happening in
Michigan since 1907 (Baker, 1983). Personnel of the Michigan Department of Natural Resources
annually perform winter track surveys in various parts of the Upper Peninsula, and tracks of this wideranging species never have been seen (e.g., Earle and Tuovila, 2002). Unverified reports of cougar were
rampant near Sleeping Bear Dunes National Lakeshore in the Lower Peninsula, yet no cougars were
found despite extensive track surveys, use of remote camera systems, baiting and thorough investigation
of reported sightings (Belant et al., 2006). The existence of such consistent disconfirmatory evidence
over the past century is difficult to reconcile with the claim of Swanson and Rusz (2006) that
a population of cougars exists in Michigan. We admit that detection of cryptic species can occur,
especially in remote areas, but we advocate that, upon finding such an odd result, initial tests be
confirmed with a second method or in another laboratory.
CONCLUSIONS
Overall, we are skeptical of the results of Swanson and Rusz (2006). Given the lack of any direct
testing of and control lanes for domestic cats and Canada lynx, failure to follow Foran et al.’s (1997)
protocol and lack of confirmatory tests, we believe that their claim to have identified multiple samples as
being produced by cougars is unsubstantiated. Inferences that there are at least eight individuals and
that these individuals are part of a population are pure speculation. Nevertheless, we agree that the
authors’ description of a partial sequence from a scat found in Delta County in 2001 (Swanson and
Rusz, 2006) appears consistent with haplotype M of cougars (Culver et al., 2000). Thus, all that we would
feel comfortable in stating, based on Swanson and Rusz (2006), is that the number of cougars
documented in the scientific literature in Michigan since the early 1900s is now one. Whether that
sample represents a released pet, a dispersing individual or a planted sample is not something that we
can assess.
Acknowledgments.—We thank V. Drietz, K. Logan, K. Pilgrim, K. McKelvey and H. Shaw for reviewing
the manuscript and R. H. Baker for providing historical insight into the question of cougars in
Michigan.

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          <elementTextContainer>
            <elementText elementTextId="1797">
              <text>6 pages</text>
            </elementText>
          </elementTextContainer>
        </element>
        <element elementId="56">
          <name>Date Created</name>
          <description>Date of creation of the resource.</description>
          <elementTextContainer>
            <elementText elementTextId="1798">
              <text>2007-10-01</text>
            </elementText>
          </elementTextContainer>
        </element>
        <element elementId="47">
          <name>Rights</name>
          <description>Information about rights held in and over the resource</description>
          <elementTextContainer>
            <elementText elementTextId="1799">
              <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>
            </elementText>
          </elementTextContainer>
        </element>
        <element elementId="42">
          <name>Format</name>
          <description>The file format, physical medium, or dimensions of the resource</description>
          <elementTextContainer>
            <elementText elementTextId="1801">
              <text>application/pdf</text>
            </elementText>
          </elementTextContainer>
        </element>
        <element elementId="44">
          <name>Language</name>
          <description>A language of the resource</description>
          <elementTextContainer>
            <elementText elementTextId="1802">
              <text>English</text>
            </elementText>
          </elementTextContainer>
        </element>
        <element elementId="70">
          <name>Is Part Of</name>
          <description>A related resource in which the described resource is physically or logically included.</description>
          <elementTextContainer>
            <elementText elementTextId="1803">
              <text>The American Midland Naturalist</text>
            </elementText>
          </elementTextContainer>
        </element>
        <element elementId="51">
          <name>Type</name>
          <description>The nature or genre of the resource</description>
          <elementTextContainer>
            <elementText elementTextId="7126">
              <text>Article</text>
            </elementText>
          </elementTextContainer>
        </element>
      </elementContainer>
    </elementSet>
  </elementSetContainer>
</item>
