ライフサイエンスコーパス: ungulate

1 280 genera grouped as 'South American native ungulates'.

2 s) or have been eradicated (e.g., introduced ungulates).

3 snails) and mature larvae, definitive hosts (ungulates).

4 ssoirs were produced on ribs of medium-sized ungulates.

5 e greater utilization and selection by large ungulates.

6 even remotely in populations of free-ranging ungulates.

7 lids, and a variety of wild and domesticated ungulates.

8 optera) were more abundant in the absence of ungulates.

9 ual synepitheliochorial placenta of ruminant ungulates.

10 fever phlebovirus in humans and domesticated ungulates.

11 migratory patterns, and demographic rates of ungulates.

12 of pregnancy losses in both humans and farm ungulates.

13 nsiting of their food, domesticated and wild ungulates.

14 microclimates, edge effects and browsing by ungulates.

15 ut how or why migratory behaviour evolved in ungulates.

16 ly whales, elephants, sirenians, and extinct ungulates.

17 is key to the foraging strategy of migratory ungulates.

18 anthropogenic activities on highly migratory ungulates.

19 nagement plans for mule deer and other large ungulates.

20 and can be applied to augmentations of other ungulates.

21 ns has been almost exclusively restricted to ungulates.

22 and multiple species of group-living African ungulates.

23 ing with the diversification of large-bodied ungulates.

24 minth life cycles and transmission involving ungulates.

25 s a major evolutionary specialization in the ungulates.

26 would be an advantage for migrating herds of ungulates.

27 expectation of increasing hunter harvests of ungulates.

28 ing a more diversified clade of mammals, the ungulates.

29 onditions as has been reported for some wild ungulates.

30 viduals, especially in large mammals such as ungulates.

31 r the hunting strategies for their main prey-ungulates.

32 environment interactions in two well-studied ungulates.

33 Indeed, comparative evidence from ungulates [9] shows that interspecific variation in coun

34 y accepted wolf density predictions based on ungulate abundance.

35 ew doors to investigate seasonal patterns of ungulate accumulations in archaeological sites using non

36 t in summer when quantified as the number of ungulates acquired per wolf per day, and least during su

37 ,111 detections of 3 large carnivores and 11 ungulates across 21,430 camera trap-nights in West Afric

38 sites is influenced by extinction risk among ungulate and carnivore hosts.

39 es for the DRB genes of primates relative to ungulate and carnivore relatives.

40 llowed greater insight into the phylogeny of ungulate and murine gammaherpesviruses.

41 oad meat diet that consisted of diverse wild ungulate and small animal species.

42 ridors can change the behaviour of migrating ungulates and diminish the benefits of migration.

43 Campylobacter fetus, a bacterial pathogen of ungulates and humans, is mediated in part by the presenc

44 ses severe disease in both domestic and wild ungulates and humans, making it a significant threat to

45 highly contagious viral disease of even-toed ungulates and is one of the most important economic dise

46 s and other arrhythmic species, such as many ungulates and large carnivores, must function in both th

47 otic infections predominantly originate from ungulates and occasionally from rats, highlighting the z

48 yaw-dominated masticatory cycle of primates, ungulates and other bunodont therians is derived; it is

49 cting mammalian hosts, particularly in apes, ungulates, and bats.

50 sister group to a large clade of carnivores, ungulates, and cetaceans.

51 portant implications for parasites of Arctic ungulates, and hence for the welfare of Arctic peoples w

52 ding enamel formation in Rangifer, and other ungulates, and how (87)Sr/(86)Sr daily intake translates

53 hreat that can be deadly to domestic or wild ungulates, and humans.

54 Our findings suggest that ungulates, and potentially other migratory species, poss

55 n the visual cortex are found in carnivores, ungulates, and primates but are not found in rodents, in

56 everal domestic sheep and goat breeds, other ungulates, and various mammal groups for sequences relat

57 groups of animals, such as fish, birds, and ungulates appear to move as a whole, exhibiting a rich b

58 Our survey confirmed that ungulates are almost always definitive hosts, and we dis

59 Wild ungulates are an important part of terrestrial ecosystem

60 Haemosporida parasites of even-toed ungulates are diverse and globally distributed, but sinc

61 Arctic ungulates are experiencing the most rapid climate warmin

62 Second, ungulates are large and long-lived, so why are they occa

63 from cells and bacteria, to birds, fish and ungulates, are mobile, and live in populations with cons

64 s to cetaceans, is a large African even-toed ungulate (Artiodactyla) that grazes and has a semiaquati

65 obtained in rodents (Rodentia) and even-toed ungulates (Artiodactyla).

66 s known that whales are related to even-toed ungulates (artiodactyls), but until now no artiodactyls

67 In even-toed ungulates (artiodactyls, including cattle), limbs are ad

68 particular concern in both wild and domestic ungulates as it causes significant neurological signs an

69 nonrecent evolutionary origins of human- and ungulate-associated HEV were projected to rodent hosts (

70 -3 years have shown that mule deer and other ungulates avoid energy infrastructure; however, there re

71 m 2015 to 2019, mimosa abundance declined as ungulate biomass recovered.

72 ults demonstrate strong cascading effects of ungulates, both trophic and nontrophic, and support the

73 insect pests, but can be severely damaged by ungulate browsing.

74 ance against herbivore feeding, particularly ungulate browsing.

75 In a perissodactyl ungulate (Burchell's zebra) the distal end of CA1 is so

76 forest canopy, which can improve forage for ungulates but also reduce snow interception, leading to

77 ons-bats are not closely related to odd-toed ungulates but instead have a more ancient origin as sist

78 (a Late Cretaceous clade related to Tertiary ungulates), but does not support Asioryctitheria (a grou

79 ificantly affects grazing livestock and wild ungulates, but also poses a threat to human health.

80 nfections and abortions in wild and domestic ungulates, but its impact on population dynamics is not

81 re mesonychians, a group of extinct, archaic ungulates, but molecular analyses have indicated that th

82 vy herbivore pressure by a widespread native ungulate can lead to rapid changes in small mammal assem

83 ortionate use of available habitats by large ungulates can alter ecosystem properties, our experiment

84 t the fear large carnivores inspire in large ungulates can cause trophic cascades.

85 There are indications that some wild ungulates can exhibit certain forms of energy saving mec

86 Heavy herbivory by ungulates can substantially alter habitat, but the indir

87 e species, particularly large carnivores and ungulates, cannot coexist with people at fine spatial sc

88 ertebrate facultative scavengers in removing ungulate carcasses from Japanese forests that lack oblig

89 ocessed numerous, relatively complete, small ungulate carcasses.

90 ns in neocortical pyramidal cells of rodent, ungulate, carnivore, and primate.

91 Furthermore, we highlight that primates, ungulates, carnivores, and bats represent significant zo

92 While sheep had an impact similar to wild ungulates, cattle have been associated with increased pl

93 We hypothesized that for ungulates, climatic conditions close to parturition have

94 ion of fish and birds, to migrating herds of ungulates, collective motion has attracted people for ce

95 re limited by food, like those of many other ungulates, commonly include more females than males.

96 Scavenged ungulates comprised 30% of mesocarnivore diets, with lar

97 erased 56.5% of the local source fauna, with ungulates comprising the most ubiquitous losses.

98 stidae' within a clade that includes archaic ungulates ('condylarths').

99 o cougar kill sites and much lower levels of ungulate consumption and carcass visitation than for coy

100 t nearly matched cougars in the magnitude of ungulate consumption.

101 ecies spanning the past 60 Myr, we find that ungulate continental assemblages exhibit prolonged ecolo

102 For many migratory ungulates, cultural inheritance maintains migration thro

103 vided a cooler thermal environment for large ungulates, decreasing operative temperature up to 16 deg

104 tential to regulate wolf populations at high ungulate densities.

105 able of supporting a substantial increase in ungulate diversity and biomass.

106 lands, grazing by large native or introduced ungulates drives ecosystem structure and function.

107 ble alternative to hunting and/or scavenging ungulates due to dental disease and/or limited prey avai

108 y weather variables known to be important to ungulate dynamics.

109 les provisioned their chicks with introduced ungulates (e.g., sheep), which were locally present in h

110 cause current culture systems cannot sustain ungulate embryo development beyond hatching.

111 support that interactions with overabundant ungulates enhance demographic success of invaders and de

112 e protected serviceberry growing in a nearby ungulate exclosure originated both before and after wolf

113 soil samples collected inside and outside of ungulate exclosures along this chronosequence and sequen

114 levels, using a series of large, long-term, ungulate-exclusion plots that span a landscape-scale pro

115 If ungulates exhibit predator-mediated foraging, burns shou

116 these long-term strategies, increasing each ungulates' exposure to risk from the alternate predator

117 In Arctic ungulates, extreme rain-on-snow and ice-locked pastures

118 s is due to a transmission barrier caused by ungulate faecal avoidance.

119 ons of 23 species of large herbivores from 5 ungulate families (Bovidae, Cervidae, Equidae, Antilocap

120 g. bats, carnivorans, odd-toed and even-toed ungulates) (Figure 1).

121 rigin of at least some South American native ungulates from 'condylarths', a paraphyletic assembly of

122 A global decline in ungulate functional diversity begins 10 Ma ago and accel

123 infect intermediate hosts prior to infecting ungulates, given that grazers could directly consume pro

124 resource availability and plant exposure to ungulate grazing over evolutionary time.

125 we show that at sites with a long history of ungulate grazing, herbivore exclusion reduced plant dive

126 analyzed for lentiviruses in the primate and ungulate groups, but no data exist for the third (feline

127 To the extent that intact ungulate guilds help to suppress populations of small an

128 However, a direct link between ungulate habitat use and their fear of large carnivores

129 ever, there remains a common perception that ungulates habituate to energy development, and thus, the

130 We find that threatened ungulates harbour a higher proportion of single-host par

131 The fear large carnivores inspire in large ungulates has been argued to have cascading effects down

132 wild ungulates, the coexistence of domestic ungulates has created a conflict over grazing resources.

133 the production of embryonic stem cells from ungulates has proved elusive.

134 of embryonic stem cells from pigs and other ungulates has proved so difficult.

135 e leading causes of death in bison and other ungulates, has not been well studied due to the lack of

136 vulnerable, and, among the large herbivores, ungulates have evolved a continuum of neonatal antipreda

137 ified six transmission routes and found that ungulate helminth parasitism has evolved some 25 times.

138 altered species interactions resulting from ungulate herbivore overabundance as a key cause of exoti

139 sts of four treatments: total-exclusion (all ungulate herbivores), mesoherbivore-exclusion (LMH >120-

140 nt of anthrax, a disease primarily affecting ungulate herbivores.

141 ytolith deposition, in response to extensive ungulate herbivory ("C(4) -grazer hypothesis").

142 13 European countries to test how changes in ungulate herbivory and eutrophication drive long-term ch

143 Dubbed "UHURU" (Ungulate Herbivory Under Rainfall Uncertainty), this exp

144 or: birds flock, bees swarm, fish shoal, and ungulates herd.

145 Characterizing patterns of range fidelity in ungulates, however, has remained challenging because of

146 provide early examples of prime-age-focused ungulate hunting, a human predator-prey relationship tha

147 For example, some migratory ungulates (i.e., hooved mammals) closely track the progr

148 However, the relative roles of climate and ungulates in alpine ecosystem change is an open question

149 Ungulates in alpine ecosystems are constrained by winter

150 a, is a major parasite of several species of ungulates in North America.

151 ration have not previously been assessed for ungulates in the tropics.

152 ion between livestock and endangered, native ungulates in these areas might impair their functioning

153 ce of different species of large herbivores (ungulates) in grasslands and savannas has fascinated eco

154 Large wild ungulates, in contrast, are seasonal breeders, as were t

155 ental events occurring following hatching in ungulates include the proliferation and maturation of ex

156 ithic (MP) hominin diets consisted mainly of ungulates, increasing evidence demonstrates that hominin

157 ls occurred multiple times, with a switch to ungulates independently from other mammalian Plasmodium.

158 ation strategy for herbivorous waterfowl and ungulates, individual songbirds in our study migrated fa

159 Our results show migratory behaviour in ungulates is an individually variable trait that can res

160 , habitat use, and social mixing of released ungulates is crucial for successful translocation and sp

161 pothesis (FMH) states that energy intake for ungulates is maximised when forage biomass is at interme

162 at the effect of forest disturbances on wild ungulates is modulated by additional factors, such as el

163 Spring migration in ungulates is of particular importance for conservation p

164 Direct egg transmission to ungulates is rare, and we suggest this is due to a trans

165 Tragulus versicolor, a diminutive species of ungulate known only from Vietnam, has been lost to scien

166 estimation techniques remain absent for most ungulates lacking identifiable marks and inhabiting rugg

167 ins putative domains similar to those of the ungulate lentiviral Tat protein.

168 se dual tropic immunodeficiency viruses, the ungulate lentiviruses, including equine infectious anemi

169 y conserved among human, simian, feline, and ungulate lentiviruses, which indicated that these epitop

170 of the Tat (transactivator) proteins of the ungulate lentiviruses.

171 y is consistent with a relationship to other ungulate-like afrotheres (Hyracoidea, Proboscidea) but d

172 e convergences are pervasive among unrelated ungulate-like placentals.

173 t, and meat was obtained by hunting the only ungulate living on the island, a small indigenous Cyprio

174 lated and used to infer a phylogeny in which ungulate malaria parasites form a monophyletic clade wit

175 e identity and evolutionary relationships of ungulate malaria parasites, we conducted Plasmodium cytb

176 ins, thought to be restricted to the hooved (ungulate) mammals and characterized by being expressed s

177 Abundance estimates inform ungulate management and recovery efforts.

178 by additional factors, such as elevation and ungulate management practices.

179 loss of multi-host parasites from threatened ungulates may be explained by decreased cross-species co

180 To minimize risk, ungulates may therefore avoid burns when and where stalk

181 eper understanding of the mechanisms driving ungulate migration and emphasize the importance of consi

182 ment affects migratory patterns, and whether ungulate migration is sufficiently plastic to compensate

183 To investigate the evolutionary origins of ungulate migration, we employed phylogenetic path analys

184 Ungulate migrations are crucial for maintaining abundant

185 Ungulate migrations generally occur along traditional ro

186 petitive forces in co-regulating large-scale ungulate migrations.

187 porating adjacent wilderness areas and known ungulate migratory routes into a protected area network

188 This suggests that changes in ungulate mobility-for instance, due to climate or land-u

189 Modern African ungulates navigate seasonal variation in resource availa

190 y size has been used successfully to explain ungulate niche differentiation with regard to food requi

191 onses to mainly diurnal human presence, with ungulate nocturnal activity increasing by 7.1%.

192 n study for 6 y in a forest where the native ungulate Odocoileus virginianus (white-tailed deer) is o

193 The effect of ungulates on arthropods was mediated by herbaceous veget

194 We examined the effects of ungulates on taxa (plants, arthropods, and an insectivor

195 ar, rainfall, which modulates the effects of ungulates on vegetation.(12) Using a long-term, large-sc

196 e associated with predation risk for African ungulates - on herbivore habitat use and (ii) establish

197 two non-human primates, four rodents, three ungulates, opossum, ferret, tree shrew, a bird, a reptil

198 Nonprimate (ungulate or feline) lentiviruses might provide safer alt

199 eliscine 'hyopsodontid' 'condylarths' (early ungulates or hoofed mammals) and extant Macroscelidea.

200 sed preference for PLA(2) domains of insect, ungulate, or metagenomic origin.

201 carnivores (order Carnivora) and terrestrial ungulates (orders Perissodactyla + Cetartiodactyla minus

202 ll measured serviceberry stems accessible to ungulates originated since wolf reintroduction, while pr

203 Although also characteristic of ungulate orthologs, such shuttling is not conserved amon

204 Hominins preyed primarily on ungulates, particularly wild goat.

205 kinds of zoogeochemical inputs deposited at ungulate parturition (placenta and natal fluid) in fores

206 We examine the effects of ungulate parturition, which often occurs synchronously d

207 n experimental clearings, demonstrating that ungulates perceived less fear from large carnivores in o

208 lengths and turning angles in a hypothetical ungulate population with contrasting population sizes an

209 Ungulate populations are increasing across Europe with i

210 A new study - on dozens of ungulate populations worldwide - demonstrates how the dy

211 Grazing mammals, ungulates, pose two evolutionary puzzles as helminth hos

212 ly tested fear of humans in wolves and their ungulate prey and quantified their nocturnality in a rep

213 nd variation of migratory behaviors in their ungulate prey can translate to dynamic wolf space use.

214 ng their superior mobility over large-bodied ungulate prey that typically sink deeper into snow.

215 For neonatal ungulate prey, risk is defined within a short temporal w

216 ions, which are well recognized to influence ungulate productivity, and provided a basis for comparin

217 phenomys), lagomorphs (Mimotona) and archaic ungulates (Protungulatum and Oxyprimus) strongly support

218 In contrast, domesticated ungulates rarely ate lianas.

219 We found that ungulate removal increased diversity of soil bacteria, w

220 the responses of soil microbes to nonnative ungulate removal remains poorly studied.

221 Ungulate responses were measured over four years, which

222 in a dataset of ten large samples of extant ungulates resulting from well-known mass mortality event

223 s displayed by extinct South American native ungulates (SANUs) confounded both Charles Darwin, who fi

224 nd parrots showed slightly male-biased BSRs; ungulates showed female-biased BSR, and primates male-bi

225 one remains dominated by the crania of large ungulates, some associated with small hearths.

226 esponses(1) in the majority of carnivore and ungulate species (n = 19) inhabiting South Africa`s Grea

227 by the trophoblast layer of the placentas of ungulate species and are inactive members of the asparti

228 We found that 95 of 207 extant ungulate species are at least partially migratory, with

229 We then predicted if the four ungulate species could efficiently utilize their food la

230 e dietary and spatial palaeoecology of these ungulate species during MIS 3, and the contemporary clim

231 ite fidelity in 669 individuals across eight ungulate species fitted with GPS collars and occupying a

232 icted to embryonic trophectoderm of ruminant ungulate species for a few days in early pregnancy.

233 Using six large ungulate species in the Rocky Mountains (USA), we evalua

234 atory behavior across 61 populations of four ungulate species on two continents (n = 1,696 individual

235 ailability in drylands reduces the number of ungulate species that will coexist.

236 resulting in skewed sex-ratios, and for many ungulate species this strategy is sustainable.

237 ement and conservation of muskoxen and other ungulate species with similar life-histories.

238 oss a large number of carnivore, primate and ungulate species, but empirical data on carnivore macrop

239 t that resource selection should vary across ungulate species.

240 ural reaction norms for three North American ungulate species.

241 rative data from wild primate, carnivore and ungulate species.

242 the three most abundant coexisting domestic ungulate species: cattle, sheep and horses.

243 test of this hypothesis in over one hundred "ungulate" species.

244 se discoveries suggest that sociality, a key ungulate strategy to reduce predation-related mortality,

245 Comparison with other ungulate studies indicates that positive associations be

246 a, isolated roads can alter the movements of ungulates such as caribou (Rangifer tarandus).

247 ns rely primarily on placental IgG transfer, ungulates such as cows and pigs depend entirely on colos

248 d a direct origin of human-associated HEV in ungulates such as swine and camelids (posterior probabil

249 the same genomic location in other even-toed ungulates suggesting that it is at least 64 million year

250 ate-predator (PDCP) interactions on neonatal ungulate survival by comparing spatial and temporal fluc

251 Among mountain ungulates, survival, a key determinant of demographic pe

252 ation in characterizing risk using carnivore-ungulate systems as a case study.

253 rey fitness, particularly in large carnivore-ungulate systems.

254 By migrating, ungulates take advantage of cyclical fluctuations in res

255 of the Late Quaternary South American native ungulate taxa Toxodon (Notoungulata) and Macrauchenia (L

256 As a small ungulate, Tc caprine offers the advantages of low cost a

257 gnificantly larger effect of cattle and wild ungulates than temperature on plant diversity.

258 ly contagious viral disease of cloven-hoofed ungulates that can lead to severe losses in the livestoc

259 rupt sensitive conservation efforts for wild ungulates that coincide with anthrax-prone landscapes.

260 itude use and activity budgets of a mountain ungulate, the Alpine chamois (Rupicapra rupicapra).

261 sland ecosystems that are habituated by wild ungulates, the coexistence of domestic ungulates has cre

262 sections of the brains of seven artiodactyl ungulates, the pyramidal layer of CA1 is four times as l

263 the adaptive genetic variation of a mountain ungulate-the Northern chamois (Rupicapra rupicapra)-coul

264 changing phenology from migratory birds and ungulates to an apex predator, further demonstrating the

265 ted the evolution of larger bodies, allowing ungulates to exploit new ecological space.

266 ross a wide range of species from rodents to ungulates to man.

267 plant phenology in mediating the ability of ungulates to surf, little is known about how drought sha

268 w, and seasonal changes in the diets of both ungulates translated into differences in their dietary o

269 Reconstructing how extinct ungulates utilized ancient landscapes provides important

270 Consistent with this finding, ungulates visited clearings 2.4 times more often than sh

271 For each ungulate, we obtain approximately 90% direct sequence co

272 g empirical data on group foraging birds and ungulates, we found a scaling relationship consistent wi

273 Ungulates were 47% more likely to run after hearing a pr

274 Site selection preferences of ungulates were quantified using resource selection funct

275 reed captive breeding programs of endangered ungulates where population growth was prioritized so tha

276 le-host parasites compared to non-threatened ungulates, which is explained by decreases in the richne

277 e most extreme examples of which are seen in ungulates, which possess an unusual elongation of the di

278 here surveys would detect a commonly studied ungulate (white-tailed deer [Odocoileus virginianus]) du

279 ly locate and count large herds of migratory ungulates (wildebeest and zebra) in the Serengeti-Mara e

280 change, our findings indicate the impact on ungulates will depend on trade-offs between enhanced sum

281 odifications of resource availability affect ungulate winter distribution, especially at their range

282 Specifically, we explored how two sympatric ungulates with different escape tactics-vertically agile

283 cially and ecologically motivated hunting of ungulates within parks and the illegal hunting of mainly

284 e visual cortex of primates, carnivores, and ungulates without assuming differences in the general vi

285 ait, adult female survival, for a threatened ungulate, woodland caribou (Rangifer tarandus caribou Gm

286 ially during the breeding season of abundant ungulates, would yield substantial benefits for wildlife