ライフサイエンスコーパス: bee

1 sitive control thiamethoxam dose (2.5 ng(-1) bee), or one of two low doses (0.377 or 0.091 ng(-1)) ba

2 We compared the genomes of 10 bee species that vary in social complexity, representing

3 but all are predicted to contain at least 5 bee species, and 46-59% of future coffee-suitable areas

4 HGD maintains genomic data for 9 bee species, 10 ant species and 1 wasp, including the ve

5 a on the spatio-temporal distributions of 91 bee species show that seasonal patterns of abundance and

6 proven a challenging pathogen to study in a bee model and interactions between viruses and the bee a

7 legs rather than in the abdomen increases a bee's moment of inertia about the roll and yaw axes but

8 c flow detectors in the central complex of a bee has inspired a new model of path integration.

9 focal apposition eye, similar to those of a bee or dragonfly.

10 ronal and behavioral plasticity underlying a bee's foraging behavior.

11 ctron Microscopy images shows that activated bee pollen carbon (ABP) is comprised of spiky, brain-lik

12 tressors by losing almost their entire adult bee population in a short time, resulting in a colony po

13 Increasing adult bee mortality had a much greater impact on colony surviv

14 nt, adults (lower dose of 0.066 microg/adult bee/day) at sublethal, field-realistic doses given over

15 any agrochemical pesticides adversely affect bee health even at sublethal levels.

16 s resulting from antibiotic exposure affects bee health, in part due to increased susceptibility to u

17 demonstrate how microbial metabolism affects bee growth, hormonal signaling, behavior, and gut physic

18 f allergen-specific B cells before and after bee venom tolerance induction.

19 IgG4-switched memory B cells expanded after bee venom exposure.

20 Neonicotinoids can alter bee navigation, but we present the first evidence that n

21 neonicotinoid alone can significantly alter bee flight.

22 s across a 75,000 km(2) region, and analyzed bee abundance, species richness, composition, and life-h

23 at they store in their colonies as honey and bee bread.

24 ied clothianidin in leaf, nectar, honey, and bee bread at organic and seed-treated farms.

25 This unique association between mite and bee persists due to the evolution of low Varroa reproduc

26 Diminished coffee suitability and bee richness (i.e., negative coupling), however, occur i

27 In our models, coffee suitability and bee richness each increase (i.e., positive coupling) in

28 n surface waters, non-target vegetation, and bee products, but the risks posed by environmental expos

29 33% of the future coffee distribution areas, bee richness decreases and coffee suitability increases.

30 To assess bee-mediated pollen dispersal on a smaller scale, we con

31 nd enzymatic activity of membrane-associated bee venom PLA2, covering a pressure range up to 2 kbar.

32 Bumble bee (Bombus) species are ecologically and economically i

33 ation systems within and outside of a bumble bee colony.

34 We found that in two alpine bumble bee species, decreases in tongue length have evolved ove

35 itored honey bee (Apis mellifera) and bumble bee (Bombus spp.) foragers in coastal California from 19

36 bers of the honey bee (Apis spp.) and bumble bee (Bombus spp.) gut microbiota.

37 ious outbreak ofN. bombiin commercial bumble bee rearing stocks in North America.

38 predict queen production and enhance bumble bee population viability.

39 e ofN. bombiand its potential role in bumble bee decline remain speculative.

40 lights the importance of interpreting bumble bee conservation efforts in the context of overall popul

41 erannual abundance of three subalpine bumble bee species.

42 Using cell cultures of the bumble bee parasite Crithidia bombi, we determined (1) growth-i

43 in its pollinators, males of the cellophane bee Colletes cunicularius [11-13].

44 In the central bee brain, the IC somata and their dendritic region, we

45 ot important in explaining twentieth century bee population trends.

46 We collected bee community data from 36 sites across a 75,000 km(2) r

47 of diversity found in Asia, where commercial bee breeding activities are low or nonexistent.

48 uggests that land use change may disassemble bee communities via different mechanisms in temperate an

49 ratios appear to be a primary factor driving bee pollen-foraging behavior and may explain observed pa

50 Melittin, the main component of dry bee venom, was used as a model amphipathic alpha-helical

51 The genetic diversity within each bee colony, particularly as a consequence of polyandry b

52 osed to multiple exposures to venom/year (eg bee keepers).

53 the widespread presence of ancient Egyptian bee iconography dating to the Old Kingdom (approximately

54 on [4], suggesting that caffeine may enhance bee reward perception.

55 thin and among populations of the euglossine bee-pollinated vine Dalechampia scandens.

56 lausible assumptions, suggested that AIT for bee and wasp venom allergy is only likely to be cost-eff

57 eated areas, with potential consequences for bee declines and pollination service delivery.

58 r in the corbiculate Electrapini as food for bee larvae (brood) and involves packing corbiculae with

59 linked with experiments and also scarce for bee pollinators.

60 scription factors involved in the shift from bee to moth pollination reside in particularly dynamic r

61 nology can play a critical role in governing bee population responses to global change.

62 o indications of Stone Age people harvesting bee products; for example, honey hunting is interpreted

63 s were more dangerous and resulted in higher bee mortality.

64 Honey bee antiviral responses include RNA interference and imm

65 Honey bee colonies exhibit an age-related division of labor, w

66 Honey bee colonies have suffered from increased attrition in r

67 Honey bee colony losses are triggered by interacting stress fa

68 Honey bee males that are infected by the parasite have Nosema

69 Many factors can negatively affect honey bee (Apis mellifera L.) health including the pervasive u

70 ounds, which can differentially affect honey bee preference.

71 in the RNA binding are conserved among honey bee iflaviruses, suggesting a putative role of the genom

72 sing on Arabidopsis and using rice and honey bee for replication.

73 hat foragers of different native Asian honey bee species can detect and use a specialized alarm phero

74 kers of the most abundant native Asian honey bee, Apis cerana and tested the responses of other bee s

75 y upon foragers and nests of the Asian honey bee, Apis cerana.

76 riod, and reveal a correlation between honey bee colony losses and national-scale imidacloprid (a neo

77 ents with double sensitization to both honey bee (HBV) and yellow jacket venom (YJV).

78 omega-6:3 ratio of pollen collected by honey bee colonies in heterogenous landscapes and in many hand

79 Here we show that pollen collected by honey bee foragers in maize- and soybean-dominated landscapes

80 wasp Lysiphlebus fabarum and the Cape honey bee Apis mellifera capensis the origin of thelytoky have

81 In the Cape honey bee it has been argued that thelytoky (th) controls the

82 an orthologs to the strongly conserved honey bee genes associated with the alarm pheromone response s

83 patients who had undergone controlled honey bee sting challenge after at least 6 months of HBV immun

84 All core honey bee intestinal bacterial genera such as Lactobacillus, B

85 from oilseed rape with those detailing honey bee colony losses over an 11 year period, and reveal a c

86 dings suggest that genetically diverse honey bee populations can recover from introduced diseases by

87 tiple interacting stressors is driving honey bee colony losses and declines of wild pollinators, but

88 tant hygienic behavior in the European honey bee (Apis mellifera L.).

89 they present a greater risk factor for honey bee health than previously suspected.

90 pathogen prevalence, as observed from honey bee colony collapse disorder.

91 in the cell line AmE-711, derived from honey bee embryos.

92 tal glycogen, lipids, and protein from honey bee workers were quantified.

93 rofiles of three stages of the haploid honey bee genome: unfertilised eggs, the adult drones that dev

94 to provide suitable plants for healthy honey bee colonies.

95 specific to mites and not to the host honey bee.

96 RNA viruses impact honey bee health and contribute to elevated colony loss rates

97 ng Virus (DWV) into the most important honey bee viral pathogen responsible for the death of millions

98 inked to the recent marked increase in honey bee colony failure, including pests and pathogens, agroc

99 nert potentiate viral pathogenicity in honey bee larvae, and guidelines for OSS use may be warranted.

100 tion sequencing, we identified VDV1 in honey bee pupae in the US.

101 ied distinct sensitization profiles in honey bee venom (HBV) allergy, some of which were dominated by

102 nses of these two pathways to 27 known honey bee pheromonal compounds emitted by the brood, the worke

103 I monitored honey bee (Apis mellifera) and bumble bee (Bombus spp.) forage

104 id on olfactory learning in the native honey bee species, Apis cerana, an important pollinator of agr

105 etter characterize the mechanism(s) of honey bee antiviral defense, bees were infected with a model v

106 e results further our understanding of honey bee antiviral defense, particularly the role of a non-se

107 Recent high annual losses of honey bee colonies are associated with many factors, including

108 -virus interaction in the induction of honey bee colony losses.

109 One form of honey bee social immunity is the collection of antimicrobial p

110 onphospholipid as a novel substrate of honey bee venom phospholipase A2.

111 hin the nest through the activities of honey bee-derived microbes and enzymes.

112 ting the observed effects of pollen on honey bee health, which incorporates the possible effects on c

113 on with escalating negative effects on honey bee immunity and health.

114 of effects of N. apis or N. ceranae on honey bee learning and memory.

115 effects of Nosema ceranae infection on honey bee microRNA (miRNA) expression, we deep-sequenced honey

116 gene expression signatures from other honey bee behaviors do not show this enrichment, nor do datase

117 (miRNA) expression, we deep-sequenced honey bee miRNAs daily across a full 6-day parasite reproducti

118 rities in humans and the highly social honey bee reflect common molecular mechanisms.

119 sects and the specific prediction that honey bee worker reproduction is driven more by patrigenes.

120 We tested the hypothesis that honey bee worker reproduction is promoted more by patrigenes t

121 Parasites and pathogens of the honey bee (Apis mellifera) are key factors underlying colony l

122 nt-binding protein 14 (OBP14) from the honey bee (Apis mellifera) has been designed for the in situ a

123 The honey bee (Apis mellifera) is commonly infected by multiple vi

124 sella alvi are dominant members of the honey bee (Apis spp.) and bumble bee (Bombus spp.) gut microbi

125 f simple ocellar photoreceptors in the honey bee allows for the necessary input for an optimal color

126 We focused here on the honey bee Apis mellifera, a social insect that relies on a wid

127 aged colonies of a single species, the honey bee Apis mellifera.

128 parasites can transmit sexually in the honey bee Apis mellifera.

129 variation in plant choice between the honey bee colonies.

130 egulate the social organization of the honey bee colony.

131 e of the three-helical junction of the honey bee dicistrovirus Israeli acute paralysis virus (IAPV) I

132 rease the nutritional diversity of the honey bee diet.

133 e generated a metatranscriptome of the honey bee gut microbiome.

134 suggest that the gut microflora of the honey bee harbours bacterial members with unique roles, which

135 varroa mite, its environment, and the honey bee host, mediated by an impressive number of cues and s

136 The honey bee is of paramount importance to humans in both agricul

137 Interestingly, the honey bee olfactory system harbors two central parallel pathwa

138 rome P450 monooxygenases (P450) in the honey bee, Apis mellifera, detoxify phytochemicals in honey an

139 cetylcholinesterase 1 (AmAChE1) of the honey bee, Apis mellifera, has been suggested to have non-neur

140 tion of the microbial community in the honey bee, as revealed by metatranscriptome sequencing, resemb

141 How can a pollinator, like the honey bee, perceive the same colors on visited flowers, despit

142 rtebrate model of social behavior, the honey bee, revealed distinct brain gene expression patterns in

143 les and addressed this question in the honey bee, the only insect in which configural learning has be

144 The honey bee, the world's most important agricultural pollinator,

145 al community to food processing in the honey bee, we generated a metatranscriptome of the honey bee g

146 resence of alternative splicing in the honey bee.

147 Therefore, we predict that this honey bee population is a ticking time-bomb, protected by its

148 g virus is an important contributor to honey bee colony losses.

149 ntimicrobial properties of honey or to honey bee defense against environmentally-acquired microorgani

150 onicotinoids brought back in pollen to honey bee hives in arable landscapes was from wildflowers, not

151 MP) is at least 20 times more toxic to honey bee larvae than to adults, but the underlying cause of t

152 ning of the economically highly valued honey bee.

153 While the natural foods of the western honey bee (Apis mellifera) contain diverse phytochemicals, in

154 ceranae is a pervasive and widespread honey bee pathogen that is associated with colony declines and

155 irus-1 (VDV1), are the most widespread honey bee viruses.

156 ortunistic stealing of honey from wild honey bee nests.

157 otics are commonly used in animal husbandry, bee-keeping, fish farming and other forms of aquaculture

158 ly intakes of 1.42-3.48 ng/bee/day) impaired bee ability to ascend.

159 We identified Eucalyptus as an important bee-forage plant particularly poor in omega-3 and high i

160 Relatively little is known about changes in bee community composition in the tropics, where pollinat

161 Increasing concentrations of clothianidin in bee bread were correlated with decreased glycogen, lipid

162 A similar shift seems to be occurring in bee forage, possibly an important factor in colony decli

163 Whereas some ubiquitous phytochemicals in bee foods up-regulate detoxification and immunity genes,

164 munological responses after stings varied in bee and vespid venom-allergic patients.

165 e to pesticide-induced changes in individual bee behaviour, but most likely due to effects at the col

166 ides lack acute toxicity, they may influence bee health by interfering with quercetin detoxification,

167 tuned to hornet threat level, of inhibiting bee departures from the safe interior of the nest.

168 s, even though the alarm pheromone itself is bee-specific.

169 composed mainly of the dicistrovirid Kashmir bee virus (KBV) was tested in cell culture, the outcome

170 restricted to a limited subset of all known bee species.

171 vely correlated with the time since the last bee sting.

172 cies of honeybee, and a solitary leafcutting bee, are strikingly similar.

173 black queen cell virus (BQCV)] in both live bee and cell culture assays, IAPV replicated to higher l

174 Season-long bee abundance and richness were not detectably different

175 We identify 139 counties where low bee abundances correspond to large areas of pollinator-d

176 aureus, with a particular focus on two major bee-derived antibacterial components, defensin-1 and hyd

177 ed for increased pathogen control in managed bee species to maintain wild pollinators, as declines in

178 Mean bee richness will decline 8-18% within future coffee-sui

179 A (from moth) with residues 2-9 of melittin (bee venom)], three fluorescence signals report oxidative

180 rst-case field-realistic dose is 0.44 microg/bee/day.

181 Strategies to mitigate bee loss generally aim to enhance floral resources.

182 Between 2008 and 2013, modeled bee abundance declined across 23% of US land area.

183 1)) and 4-oxo-decanoic acid (4-ODA, 13.3 mug bee(-1)) at a 0.78 ratio of 4-OOA/4-ODA.

184 ds were 4-oxo-octanoic acid (4-OOA, 10.4 mug bee(-1)) and 4-oxo-decanoic acid (4-ODA, 13.3 mug bee(-1

185 We explored how the biodiversity of native bee species changes across forested, agricultural, and u

186 by neonicotinoids on a broad range of native bee species deserve further study.

187 e used globally, but their effects on native bee species are poorly understood.

188 f S. alvi were able to colonize their native bee host but not bees of another genus.

189 Here, we present a new bee species that excavates sandstone nests, Anthophora (

190 a single imidacloprid dose as low as 0.1 ng/bee had significantly reduced olfactory learning acquisi

191 exposed as larvae to a total dose of 0.24 ng/bee did not have reduced survival to adulthood.

192 Acute consumption (1.34 ng/bee) impaired locomotion, caused hyperactivity (velocity

193 f consuming a single sublethal dose (1.34 ng/bee), foragers showed excitation and significantly incre

194 field-relevant daily intakes of 1.42-3.48 ng/bee/day) impaired bee ability to ascend.

195 -relevant thiamethoxam doses of 1.96-2.90 ng/bee/day.

196 Bomblyiid flies were the most effective non-bee flower visitors.

197 but also in shifts in seasonal abundance of bee pollinators.

198 ding a geochronologic midpoint assessment of bee pollen-collection strategies.

199 neonicotinoids causing a reduced capacity of bee species to establish new populations in the year fol

200 ect the specific ecological circumstances of bee foraging.

201 M) to predict physicochemical composition of bee pollen mixture given their botanical origin.

202 the published literature a global dataset of bee diversity at sites facing land-use change and intens

203 nicotinoids are implicated in the decline of bee populations.

204 he ImmunoCAP system for routine diagnosis of bee venom (BV) allergy.

205 ferred floral resources is the key driver of bee decline because accurate assessment of host plant pr

206 cent results on the potential involvement of bee gut communities in pathogen protection and nutrition

207 icotinoids could scale up to cause losses of bee biodiversity.

208 f bird diversity, along with major losses of bee diversity.

209 ysicochemical characteristic of a mixture of bee pollen, given their botanical origin, fuzzy models p

210 The distinct morphologies of bee pollens and cattail pollens are resembled on the fin

211 impact on colony survival than mortality of bee larvae or reduction in egg laying rate.

212 erences with intensive field observations of bee foraging.

213 Declining populations of bee pollinators are a cause of concern, with major reper

214 We determined host plant preference of bee species using pollen loads on specimens in entomolog

215 The geographical range of bee product exploitation is traced in Neolithic Europe,

216 Here, we investigated the putative role of bee venom (Bv) in human FOXP3-expressing Treg homeostasi

217 No previous study of bee spatial navigation has been able to follow animals'

218 atlas data to quantify population trends of bee species and their host plants.

219 ly aligned with body orientation) typical of bee flight, a feature not captured in any previously pro

220 This review takes a holistic view of bee toxicology by taking into account the spectrum of xe

221 nd because coffee production is dependent on bee pollination.

222 statistically significant, and dependent on bee size.

223 nicotinoid insecticides as seed dressings on bee-attractive crops.

224 c-induced dysbiosis (microbial imbalance) on bee health and susceptibility to disease has not been fu

225 d enforcing effective quarantine measures on bee movements are all practical measures that should be

226 attention to the impact of the microbiota on bee health.

227 des, and in particular of neonicotinoids, on bee health remain much debated.

228 melittin, the active molecule of apitoxin or bee venom, were investigated on human red blood cells (R

229 on of some flying insects [3-5]-of an orchid bee, Euglossa imperialis.

230 f large ocellar L-neurons in the male orchid bee Euglossa imperialis.

231 tied to the remarkably high number of orchid bee species coexisting together in some neotropical comm

232 A specialist orchid-bee study combining herbarium, museum and field data sho

233 pis cerana and tested the responses of other bee species to these alarm signals.

234 how adverse effects of imidacloprid on queen bee fecundity and behavior and improves our understandin

235 ect centering behaviour as found in the real bee's behaviour.

236 noculating a mixture of iflavirids [sacbrood bee virus (SBV), deformed wing virus (DWV)] and dicistro

237 bial pollen baskets (corbiculae) of the same bee taxa from a taxonomically much narrower suite of arb

238 Whereas the olfactory systems of several bee and ant species have been well characterized, very l

239 Many of them, including slow bee paralysis virus (SBPV), cause lethal diseases in hon

240 owed that MV is most closely related to Slow bee paralysis virus (SBPV), which is highly virulent in

241 l aspects of size regulation in the solitary bee, Osmia lignaria We demonstrate that starvation cues

242 ortant given concerns about declines in some bee species.

243 ncluding the nectar-providing plant species, bee species, geographic area, and harvesting conditions.

244 0 K) or 40,000 (40 K) live N. ceranae spores/bee, Vg titers were significantly elevated by + 83% and

245 ingless bee honey samples, from 11 stingless bee species, were examined.

246 Twenty-eight stingless bee honey samples, from 11 stingless bee species, were e

247 t dissimilar to those reported for stingless bee honeys from the neo-tropics.

248 vely subordinate to group-foraging stingless bee species.

249 the physicochemical properties of stingless bee honey from SE Asia (Thailand).

250 We compared functional traits of stingless bee species found in pastures surrounded by differing am

251 with the Apis mellifera standard, stingless bee honey is characterized as possessing higher moisture

252 ate bee communities, we found that stingless bee species with the widest diet breadths were less like

253 ependently in Mesoamerica with the stingless bee Melipona beecheii, as documented by archaeological f

254 fferent members of a colony of the stingless bee Melipona scutellaris.

255 Stingless-bee honeys contained more water and less total sugars an

256 Increasing production of stingless-bee honey and the prospect of broader marker for natural

257 g with electrophoresis profiles of stingless-bee honeys proteins could be an alternative for determin

258 n designing conservation habitats supporting bee populations.

259 o both theoretical predictions and temperate bee communities, we found that stingless bee species wit

260 Temporally, we demonstrate that bee products were exploited continuously, and probably e

261 finding was explained by demonstrating that bee venom-derived phospholipase A2 (PLA2) activates T ce

262 herbarium, museum and field data shows that bee flight dates are advancing faster than orchid flower

263 roactive levels to their site of action: the bee brain.

264 del and interactions between viruses and the bee antiviral immune response remain poorly understood.

265 We used QTL mapping in hybrids between the bee-pollinated monkeyflower Mimulus lewisii and the clos

266 nwhile, nest defenders were triggered by the bee alarm pheromone and live hornet presence to heat-bal

267 umans in intelligence - rather he saw in the bee a qualitatively different form of intelligence, tail

268 gical recording of olfactory circuits in the bee brain to determine whether mushroom bodies (MBs), br

269 for estimating angular velocity (AV) in the bee brain, capable of quantitatively reproducing experim

270 to the information processing regions in the bee brain.

271 bees, indicating an earlier evolution in the bee lineage.

272 CREB (Apis mellifera CREB, or AmCREB) in the bee's division of labor.

273 eas nectar is stored in the abdomen near the bee's center of mass, pollen is carried on the hind legs

274 an important role for the regulation of the bee antiviral immune response by ATP-sensitive inwardly

275 urons converge in the central complex of the bee brain, and through block-face electron microscopy, w

276 plant sources and use in the defense of the bee community.

277 Detailed morphology of the bee proboscis is shown to be finely adjusted to the flor

278 These findings indicate that the bee gut microbiota has basic roles similar to those foun

279 structures and neuronal responses within the bee brain and subsequently compared their ability to gen

280 Land-use change and intensification threaten bee populations worldwide, imperilling pollination servi

281 ects of neonicotinoid-treated crops on three bee species across three countries (Hungary, Germany, an

282 ether migratory management is detrimental to bee health.

283 Levels of sIgE and sIgG4 to bee and vespid venom, rApi m 1, and rVes v 5 were measur

284 serological markers to predict tolerance to bee and vespid stings.

285 Using bee and wasp venom responses as a model system, we inves

286 Honey is generated by various bee species from diverse plants, and because the value o

287 treadmill paradigm with a tethered, walking bee was successful as bees exhibited robust discriminati

288 ange and intensification, and assess whether bee responses to these pressures vary across 11 regions

289 Wild bee declines have been ascribed in part to neonicotinoid

290 sion of RNA viruses between managed and wild bee pollinators, pointing to an interconnected network o

291 quantified expert knowledge to estimate wild bee abundance and associated uncertainty.

292 We relate 18 years of UK national wild bee distribution data for 62 species to amounts of neoni

293 ighlight the species-specific nature of wild bee decline and indicate that mitigation strategies will

294 secticides to losses of the majority of wild bee species.

295 These areas of mismatch between supply (wild bee abundance) and demand (cultivated area) for pollinat

296 biogeographical regions, crop-visiting wild bee communities are dominated by a small number of commo

297 was one of two main factors associated with bee decline.

298 vespid venom, but not in those treated with bee venom.

299 uous behavioural information for each worker bee.

300 Over 8 years, bee abundances were driven primarily by the indirect eff