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1 wers of bowerbirds or the engineered dams of beavers.
2 high occurrence of T. gondii infection in UK beavers.
3 ith dams reconstructed by newly recolonizing beavers.
6 n stock loss resulting from both logging and beaver activities in Chilean Tierra del Fuego from 1986
10 fire; changes in shoreline inundation due to beaver activity); this lake lacked overall trends in MeH
11 have been found to be positively impacted by beaver activity, yet the causal drivers were unknown.
12 dii DNA was detected in 19/23 (83%) Eurasian beavers; all consistent with PCR-RFLP ToxoDB#3 with limi
13 scale experiment to quantify the benefits of beavers and BDAs to a fish population and its habitat.
14 es in fruit flies, degus, birds, fish, bats, beavers and humans; however, studies in rats and hamster
15 estern U.S. will further expand the range of beavers and magnify their impacts on watershed hydrology
16 coincides with the extinction of terrestrial beavers and raises the question whether the two events h
18 red with the expanding range of the American beaver-and their dams, which transform hydrologic and bi
19 hydrology, sediment storage, and vegetation, beaver are widely acknowledged as ecosystem engineers.
20 tion of beaver lodges would reflect seasonal beaver behavior, intensifying through the ice-free seaso
21 Our results show that pioneer inundation by beavers can increase MeHg concentrations in streams, but
23 reuse) of ponds constructed by the Eurasian beaver Castor fiber in regulating MeHg concentrations in
28 al mitochondrial genome of the extinct giant beaver Castoroides and estimate the origin of aquatic be
29 d delta(15)N) of coeval subfossil plants and beaver collagen (Dipoides sp.) from the Early Pliocene,
30 ley bottoms with old-growth forest or active beaver colonies store the great majority of above- and b
31 do not support the hypothesis that the giant beaver consumed trees or woody plants, which suggests th
32 re detected in McLean Creek (30.1 mug/L) and Beaver Creek (190 mug/L), two tributaries that are physi
34 , we genotyped a subset of subjects from the Beaver Dam (WI) Eye Study and performed a model-free gen
36 shed-scale experiment to test how increasing beaver dam and colony persistence in a highly degraded i
38 thors utilize data from the population-based Beaver Dam Eye Study (1988-2000) to examine this possibi
39 ng risk of death, was similar to that of the Beaver Dam Eye Study (BDES) after age standardization.
40 Presented are new GWS data from the full Beaver Dam Eye Study (BDES) family cohort, including lon
42 (1) 325 individuals (225 sib pairs) from the Beaver Dam Eye Study (BDES), and (2) 297 individuals (34
43 ertained population-based family cohort, the Beaver Dam Eye Study (BDES), which was also used to asse
46 s (102 families; n = 224 sib pairs) from the Beaver Dam Eye Study and performed a model-free genome-w
47 5- and 10-year follow-up examinations of the Beaver Dam Eye Study cohort were digitized, and optical
50 icipants aged 63 to 102 years at the 20-year Beaver Dam Eye Study follow-up examination in 2008-2010,
52 pedigrees who participated in the 1988-1990 Beaver Dam Eye Study in Wisconsin to determine whether t
55 in our population was similar to that of the Beaver Dam Eye Study population (0.98% [95% CI, 0.49-1.8
57 in our previous genome scan for ARMD, in the Beaver Dam Eye Study sample (D15S659, multipoint P=.047)
59 ipants (aged 43-86 years at baseline) in the Beaver Dam Eye Study were evaluated every 5 years during
60 e-related maculopathy (ARM) in people in the Beaver Dam Eye Study who were aged 43-86 years (n = 3,68
61 volved a random sample of 975 persons in the Beaver Dam Eye Study without signs of AMD who participat
64 line examination and 5-year follow-up of the Beaver Dam Eye Study, Beaver Dam, Wisconsin (1988-1990 a
73 .2% progressed and 4.9% regressed, using the Beaver Dam grades; progression occurred in 4.9% to 9.9%,
74 1.9% progressed and 3.2% regressed using the Beaver Dam grades; progression occurred in 8.0% to 19.7%
75 in riparian hydraulic gradients imposed by a beaver dam is 10.7-13.3 times greater than seasonal hydr
76 pidemiology of Hearing Loss Study (EHLS) and Beaver Dam Offspring Study (BOSS), a pair of studies of
77 arch 1, 1993, through June 15, 1995) and the Beaver Dam Offspring Study (June 8, 2005, through August
78 eline) and a sample of participants from the Beaver Dam Offspring Study (n = 2,173; ages > or =45 yea
79 GN, SETTING, AND PARTICIPANTS: Data from the Beaver Dam Offspring Study, a longitudinal cohort study
80 ed with the HIV-uninfected population in the Beaver Dam Offspring Study, there was an approximate 4-f
85 pulation-based studies examined residents of Beaver Dam, Wisconsin, aged 43 to 84 years in 1987 throu
87 eye diseases was conducted in 1988--1990 in Beaver Dam, Wisconsin, and a follow-up examination was p
88 ing in age from 43 to 84 years and living in Beaver Dam, Wisconsin, at the time of a census (1987-198
89 ing in age from 43 to 84 years and living in Beaver Dam, Wisconsin, at the time of a census (1987-198
90 l people 43 to 84 years of age and living in Beaver Dam, Wisconsin, in 1988 were invited for a baseli
91 l people 43 to 84 years of age and living in Beaver Dam, Wisconsin, in 1988 were invited for a baseli
93 All persons aged 43 to 84 years of age in Beaver Dam, Wisconsin, were invited for a baseline exami
94 ars of age living in the city or township of Beaver Dam, Wisconsin, were recruited from 1987 through
99 an extreme flooding event destroyed several beaver dams and resulted in the loss of breeding habitat
101 the hypothesis that this extinct semiaquatic beaver engaged in woodcutting behaviour for feeding purp
102 nificant positive impacts on bat foraging at beaver-engineered sites, and increases in species richne
103 bitat heterogeneity and food availability in beaver-engineered streams foster bat richness, activity
106 ~ 1980 imagery, and there is no evidence of beaver engineering in ~ 1952 imagery, consistent with ob
107 creased arthropod prey abundance) impacts of beaver engineering on bats, the authors found mixed resp
108 -hunting aerial hawkers benefitted most from beaver engineering, and increased standing deadwood dens
110 how the scale and magnitude of northwestward beaver expansion in Alaska, indicated by the constructio
111 systems, inundated for the first time since beaver extirpation, and seven were recolonized, with dam
116 emiaquatic Miocene castorid, suggesting that beavers have been consuming woody plants for over 20 mil
120 These dietary preferences rendered the giant beaver highly dependent on wetland habitat for survival.
122 logy of the northward dispersal of the giant beaver in Beringia, indicating a correlation with ice sh
123 re expect that the recovery and expansion of beavers in the boreal system will only have a transition
124 gate the presence and impact of T. gondii on beavers in the United Kingdom, archived brain, heart, an
134 om, archived brain, heart, and liver from 23 beavers necropsied between 2021 and 2023 were screened f
136 es sp.) from the Early Pliocene, High Arctic Beaver Pond fossil locality (Ellesmere Island), in order
137 (Protarctos abstrusus) were collected at the Beaver Pond fossil site in the High Arctic (Ellesmere I.
143 y pronounced in large parts of Europe, where beaver populations have expanded rapidly following near-
144 es key evidence for the positive outcomes of beaver reintroductions on local biodiversity, highlighti
145 ghted two tributaries to the Athabasca River-Beaver River and McLean Creek-as possibly receiving OSPW
147 erences between a weak (mouse) and a strong (beaver) SIRT6 protein and identified five amino acid res
148 Smart-seq3 scRNA-seq data, firmly show that Beaver substantially outperforms existing meta-assembler
149 abitat selection to increase encounters with beavers, supporting previous work demonstrating the impo
151 entrations in pioneer but not in recolonized beaver systems were up to 3.5 fold higher downstream tha
154 intensifying through the ice-free season as beaver vulnerability increases as they spend more time a
157 ift supports wolf prey-switching behavior to beavers when their primary prey, moose, are more difficu