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Optimal central-place foraging by beavers: Tree-size selection in relation to defensive chemicals of quaking aspen

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Abstract

At a newly occupied pond, beavers preferentially felled aspen smaller than 7.5 cm in diameter and selected against larger size classes. After one year of cutting, 10% of the aspen had been cut and 14% of the living aspen exhibited the juvenile growth form. A phenolic compound which may act as a deterrent to beavers was found in low concentrations in aspen bark, and there was no significant regression of relative concentration of this compound on tree diameter. At a pond which had been intermittently occupied by beavers for over 20 years, beavers selected against aspen smaller than 4.5 cm in diameter, and selected in favor of aspen larger than 19.5 cm in diameter. After more than 28 years of cutting at this site, 51% of the aspen had been cut and 49% of the living aspen were juvenileform. The phenolic compound was found in significantly higher concentrations in aspen bark than at the newly occupied site, and there was a significant negative regression of relative concentration on tree diameter. The results of this study show that responses to browsing by trees place constraints on the predictive value of standard energy-based optimal foraging models, and limitations on the use of such models. Future models should attempt to account for inducible responses of plants to damage and increases in concentrations of secondary metabolites through time. Peer Reviewed http://deepblue.lib.umich.edu/bitstream/2027.42/47775/1/442_2004_Article_BF00379963.pdf
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... Beaver activity affects not only the proportion of species but also the structure of waterbank vegetation (Jones et al., 2009;Mahoney & Stella, 2020). Different diameter classes are often utilized at different ratios, and diameter selectivity may differ among taxa (Basey et al., 1988;Haarberg & Rosell, 2006;Jackowiak et al., 2020). Thus, the utilization of certain diameter classes of a given taxon may also be relevant to biological invasion, if the diameterclass distribution of native and invasive species is not the same. ...
... Certain tree species produce certain metabolites in different proportions at different plant ages (that is, in trees with different diameters) (Wam et al., 2017), which may influence the beaver's diameter selectivity and its differences within the taxa (Basey et al., 1988). ...
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Herbivore species can either hinder or accelerate the invasion of woody species through selective utilization. Therefore, an exploration of foraging decisions can contribute to the understanding and forecasting of woody plant invasions. Despite the large distribution range and rapidly growing abundance of beaver species across the Northern Hemisphere, only a few studies focus on the interaction between beavers and invasive woody plants. We collected data on the woody plant supply and utilization at 20 study sites in Hungary, at two fixed distances from the water. The following parameters were registered: taxon, trunk diameter, type of utilization, and carving depth. Altogether 5401 units (trunks and thick branches) were identified individually. We developed a statistical protocol that uses a dual approach, combining whole‐database and transect‐level analyses to examine foraging strategy. Taxon, diameter, and distance from water all had a significant effect on foraging decisions. The order of preference for the four most abundant taxa was Populus spp. (softwood), Salix spp. (softwood), Fraxinus pennsylvanica (invasive hardwood), and Acer negundo (invasive hardwood). The diameter influenced the type of utilization, as units with greater diameter were rather carved or debarked than felled. According to the central‐place foraging strategy, the intensity of the foraging decreased with the distance from the water, while both the taxon and diameter selectivity increased. This suggests stronger modification of the woody vegetation directly along the waterbank, together with a weaker impact further from the water. In contrast to invasive trees, for which utilization occurred almost exclusively in the smallest diameter class, even the largest softwood trees were utilized by means of carving and debarking. This may lead to the gradual loss of softwoods or the transformation of them into shrubby forms. After the return of the beaver, mature stages of softwood stands and thus the structural heterogeneity of floodplain woody vegetation could be supported by the maintenance of sufficiently large active floodplains. The beaver accelerates the shift of the canopy layer's species composition toward invasive hardwood species, supporting the enemy release hypothesis. However, the long‐term impact will also depend on how plants respond to different types of utilization and on their ability to regenerate, which are still unexplored issues in this environment. Our results should be integrated with knowledge about factors influencing the competitiveness of the studied native and invasive woody species to support floodplain conservation and reconstruction.
... Cafeteria experiments performed by Basey et al. [52,53] showed that aspen resprout growth following beaver felling of trees was highly avoided by beavers relative to controls. They also found that an unidentified phenolic compound was about 18 times greater in the avoided resprout growth, which strongly suggests that the induction of phytochemical defenses deterred subsequent beaver herbivory. ...
... Previous research has shown that herbivory induces defensive (i.e., tannins and phenolic glycosides) and nutritional (i.e., carbon and nitrogen) chemistry in woody plants [12,52,53,57,58]. With narrowleaf cottonwood, Body et al. [59] found that the presence of the gall-forming aphid Pemphigus betae Doane, 1900, triggered the induction of 15 different phytohormones belonging to 5 different classes. ...
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... Transects: WBT-waterbank transect, OT-outer transect the fact that the time and work required for cutting down, processing, and mobilizing a tree increases with trunk diameter (Fryxell and Doucet 1991;Gallant et al. 2004). Avoidance of the thinnest units may be explained by the higher concentration of certain chemical substances with anti-herbivore properties in the younger units and shoots (Basey et al. 1988). In line with the results of our previous research conducted in active floodplains of larger rivers (Juhász et al. 2022), we found that the utilized trunk diameter range of the preferred Salix and Populus species was wider than that of other species. ...
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... Beavers are based out of a central location, the majority of foraging activities take place in the 50 m buffer around water bodies, and they transport food not immediately consumed back to the same location (Stoffyn-Egli & Willison, 2011). Thus, they are centralplace foragers, which limits their dispersion into new areas and may complicate analysis of habitat selection (McGinley & Whitham, 1985;Basey et al., 1988;Basey & Jenkins, 1995;Raffel et al., 2009;Hood, 2020). Additionally, habitat selection by beavers in one study usually cannot be directly applied to another area, as important habitat variables may vary depending on spatiotemporal scale and ecological setting Touihri et al., 2018;Hood, 2020). ...
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Warming of the Arctic is leading to permafrost degradation, increased vegetation cover, earlier breakup of ice on rivers and lakes, and the arrival and northward expansion of new wildlife species. Beaver expansion into the Arctic has been attributed to shrubification and observed to impact the hydrology, permafrost, wildlife, and people of these regions. The objectives of this research were to 1) characterize changing beaver distribution and associated habitat characteristics in Nunavik, 2) document Inuit knowledge about beaver expansion and the impact on Inuit food security, and 3) identify adaptation strategies to minimize these impacts, while co-producing this knowledge through regional and local research partnerships and collaboration. A mixed methods and knowledge co-production research approach, which included Inuit knowledge interviews, helicopter survey of beaver lodges, dams, and food caches, community questionnaires, and habitat selection analysis, indicated that communities prioritized beaver management because of their concerns regarding the impact of beaver dams on Arctic char and associated impacts on food security. The earliest observations of beavers in the Ungava region of Nunavik occurred near Kangiqsualujjuaq in the late 1950s and near Kuujjuaq in the 1970s, with more recent observations confirming beaver presence much farther north near Aupaluk and Kangirsuk. A habitat selection analysis underlined the importance of dominant water body type as a predictor of beaver presence at both a landscape and local scale of analysis, with beaver sign most often observed along streams, then rivers, then small lakes and less commonly on large lakes. The findings demonstrate how species expansion can be better monitored by integrating western science and Inuit knowledge. Inuit observations can detect beaver impacts on other species, are sensitive to small changes, and can capture transient events, such as sightings of beavers unsuccessfully attempting to colonize a new habitat. Helicopter surveys cover larger areas than Inuit may be able to travel by land and provides systematic information on presence and absence at one point in time. Increased awareness of the distribution of beavers, associated habitat variables, and possible future colonization routes achieved through knowledge co-production can help Inuit policy makers mitigate and adapt to changing wildlife distributions and hydrological regimes.
... On the other hand, due to their short-term exposure (e.g., saplings), relatively low biomass, and low density in some stands, trees with smaller diameters were sometimes "avoided", probably due to the greater energy expenditure required to obtain them in such stands, and larger diameters were preferred, as in the case of oak or hazel. In addition, woody plant shoots that have been repeatedly felled may contain relatively high amounts of toxic secondary substances [48][49][50]. Finally, beavers have no natural predators at these sites, which generally affects beaver foraging [51,52], hence they can afford to expend more energy and time felling larger woody plants to obtain the greater biomass available from the crowns of mature woody plants. ...
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... While the propagating effects of beaver activity can be beneficial, careful consideration must be given to whether the history of a given watershed is naturally "tuned" to beaver ecology. For example, in areas where beaver has been introduced, trees often lack defensive mechanisms and reproductive strategies that occur in forests that are regularly subject to beaver activity because they do not share a common evolutionary history (Basey et al., 1988;Martínez Pastur et al., 2006;Anderson et al., 2009). Introduced beaver may be particularly devastating for systems invaded by other non-native species, as novel disturbance has the potential to drive feedback loops that favor survivorship of other invaders, promote new introductions or spread, and overwhelm any biotic resistance that might be perpetrated by native species (i.e., invasional meltdown: Simberloff and Von Holle, 1999;Crooks, 2002;Maret et al., 2006;Braga et al., 2018). ...
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