Immediate increase in isotopic enrichment in small mammals following the expansion of a great cormorant colony
Colonies of great cormorants (<i>Phalacrocorax carbo</i>) impact terrestrial ecosystems through the transport of nutrients from aquatic to terrestrial ecosystems. Deposited guano overload the ecosystem with N and P, change soil pH and damage vegetation. The ways in which small mammals...
Main Authors: | , , , , |
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Format: | Article |
Language: | English |
Published: |
Copernicus Publications
2018-06-01
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Series: | Biogeosciences |
Online Access: | https://www.biogeosciences.net/15/3883/2018/bg-15-3883-2018.pdf |
Summary: | Colonies of great cormorants (<i>Phalacrocorax carbo</i>) impact
terrestrial ecosystems through the transport of nutrients from aquatic to
terrestrial ecosystems. Deposited guano overload the ecosystem with N and P,
change soil pH and damage vegetation. The ways in which small mammals are
impacted, however, are little known. We aimed to evaluate the effects of an
expanding great cormorant colony, testing if the expansion immediately
increased the input of biogens into the forest ecosystem and, further, if the
growing influence of the colony was reflected in basal resources (plants and
invertebrates) and the hair of small mammals. <i>δ</i><sup>15</sup>N and
<i>δ</i><sup>13</sup>C signatures were analyzed in granivorous yellow-necked mice
(<i>Apodemus flavicollis</i>), omnivorous bank voles (<i>Myodes
glareolus</i>) and basal resources of animal and plant origin from the territory
of a colony of great cormorants situated near the Baltic Sea in west
Lithuania. We found that biogens transferred by great cormorants to the
terrestrial ecosystem affected the potential foods of the small mammals and
led to highly elevated and variable <i>δ</i><sup>15</sup>N values. An increase of the
size of the colony in 2015 resulted in isotopic enrichment of the small
mammals in the zone of expansion in comparison to levels in 2014. The
increase of <i>δ</i><sup>15</sup>N in <i>A. flavicollis</i> was 7.5 %
(<i>p</i> < 0.05) in the ecotone and 5.7 % in the expansion zone. The
decrease in <i>δ</i><sup>13</sup>C signatures in <i>A. flavicollis</i> was 4.5 % (<i>p</i> < 0.1)
in the expansion zone and 3.1 % (<i>p</i> < 0.001)
in the colony. In <i>M. glareolus</i>, the decrease in <i>δ</i><sup>13</sup>C
signatures was 8.5 % in the expansion zone, 3.3 % (<i>p</i> < 0.1) in
the control zone and 2.6 % in the ecotone. Isotopic niches (central
ellipses) of <i>A. flavicollis</i> in the colony and between the control
and expansion zones were separated in 2014 and 2015, while they partially
overlapped in the ecotone. The isotopic niches of <i>M. glareolus</i> in
2014 and 2015 were separated in the ecotone and had a small overlap in the
colony. For most of the resources tested, the isotopic signatures in the
established colony area were significantly higher than in the rest of
cormorant-inhabited area. In the colony, the <i>δ</i><sup>15</sup>N values in plants
(16.9 ± 1.1 ‰) were higher than in invertebrates
(13.6 ± 0.4 ‰). In the ecotone, the <i>δ</i><sup>15</sup>N
values were 12.0 ± 1.4 in plants and 14.7 ± 0.04 ‰ in invertebrates, while in the expansion zone they
were 7.2 ± 3.0 and 9.9 ± 3.8 ‰, respectively. <i>δ</i><sup>15</sup>N-rich resources led to
increased <i>δ</i><sup>15</sup>N values in the hair of <i>A. flavicollis</i> and
<i>M. glareolus</i>. Thus, biogens from the great cormorant colony
immediately affected small mammals through their food sources. |
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ISSN: | 1726-4170 1726-4189 |