ライフサイエンスコーパス: gull

1 human and animal populations, including wild gulls.

2 13 and H16 LPAIVs that circulate globally in gulls.

3 from long-range transport in glaucous-winged gulls.

4 only slightly influenced total mortality in gulls.

5 eviously in eggs of wild Great Lakes herring gulls.

6 The gull abatement BMP was associated with improved beach wa

7 time on the breeding grounds, in contrast to gull AIV data from other geographic regions.

8 Muscovy ducks, Mallards, Whistling Swans and gulls also emphasizing industrial impacts for the human-

9 Extracts from CHSH and GULL altered 15 and 13 of 27 genes on the PCR array comp

10 Hg concentrations in gull and Common Tern eggs were generally below generic t

11 PB-DiPhOBz metabolites were detectable after gull and rat microsomal assay incubation with solutions

12 ane (HBCD) isomers were studied for glaucous gull and ringed seal from East Greenland.

13 (OC) compounds were determined for glaucous gull and ringed seal samples collected from the same are

14 ers in Charadriiformes (plovers, sandpipers, gulls and auks).

15 d relatively more brown lemmings compared to gulls and hawks.

16 emperate radiations including the waterfowl, gulls and woodpeckers.

17 d microbial source tracking (MST) for human, gull, and canine fecal sources, monitoring of enterococc

18 -nesting sentinel seabird, the yellow-legged gull, and measured antibody levels against three pathoge

19 g response rates for Charadriiformes (terns, gulls, and auks), primarily with social attraction.

20 avian species.IMPORTANCEMigratory waterfowl, gulls, and shorebirds are natural reservoirs for influen

21 tro, and also indicated that if wild herring gulls are exposed (e.g., via the diet) to photolytic pro

22 Because gulls are mobile and can shed antimicrobial-resistant ba

23 Gulls are often cited as important contributors of fecal

24 Gulls are often described as strong urban adapters, but

25 we conducted an experiment to assess whether gulls are readily colonized with mcr-1 positive E. coli,

26 arkers, leading to recommendations to manage gulls as a pollutant source.

27 ests, with only the RIPA and the Organon and Gull assays identifying reactive specimens.

28 a significant reduction in the density of a gull-associated marker was observed (p < 0.001).

29 suggested FIB exceedances could be traced to gulls based on gull marker prevalence and correlations w

30 on the survival of adult great black-backed gulls, both directly and through effects of individuals'

31 nt-use flame retardants (FRs) in ring-billed gulls breeding in a highly industrialized section of the

32 Nine OPs accumulated in herring gulls, but the concentrations and proportions of OPs wer

33 dults of Scopoli's shearwaters and Audouin's gulls (ca. 28% and 23% of total mortality, respectively)

34 rtality, respectively) and also for immature gulls (ca. 90% of mortality).

35 Further, a trimmed gull can use its wing joints to control the frequencies

36 Here, we fill this gap by quantifying how a gull can use wing morphing to adjust its longitudinal dy

37 Our results suggest that yellow-legged gulls can be a useful sentinel population of locally tra

38 s, and pathogens measured in seawater and in gull, cat, and raccoon feces.

39 nce for high quality forage fish) and silver gulls Chroicocephalus novaehollandiae (efficient flyer,

40 Individual eggs from 2 other herring gull colonies, north and south Pukaskwa National Park, L

41 , which has resulted in an increase in human-gull conflicts.

42 ities were also significantly reduced during gull control (p < 0.001 and p = 0.012, respectively for

43 cteria were detected on 64% of days prior to gull control and absent during gull intervention, a sign

44 ers, and some recreational beaches have used gull control measures to improve microbial water quality

45 nic bacteria were measured before and during gull control using culture methods and quantitative poly

46 arassment by dogs was an effective method of gull control: average daily gull populations fell from 6

47 s showed that as flight speed increases, the gull could fold or sweep its wings backward to trim.

48 Because gulls could disseminate the mcr-1 gene, we conducted an

49 Godwit broods may avoid areas of higher gull densities when chicks are susceptible to gull preda

50 conspecifics, earlier hatch dates and lower gull densities, whereas older chicks survived better wit

51 gen isotope tracers reflected a shift of the gull diet from aquatic to more terrestrial origins, and

52 oportions of aquatic and terrestrial food in gull diets.

53 We observed peak prevalence in large gulls during the autumn migration (5.3-9.8%), but peak p

54 Concomitantly, godwit broods avoided gulls early in development and when godwit densities wer

55 this study, graded concentrations of herring gull egg extracts, collected from five Great Lakes breed

56 E and temporal and spatial trends in herring gull egg pools and individuals from 14 colony sites acro

57 air, precipitation, lake trout, and herring gull egg samples throughout the sampling periods.

58 s in standard mixtures, spiked hen eggs, and gull egg samples, where these compounds tend to accumula

59 ern Alberta, Hg concentrations in California Gull eggs declined significantly through time.

60 Herring gull eggs from Channel Shelter Island (CHSH, Lake Huron)

61 crimination of variably contaminated herring gull eggs from the Great Lakes.

62 equency of OPEs in all European starling and gull eggs was lower than 16%.

63 In gull eggs, the median summation operatorVMS concentratio

64 thoxylated PBDPBs in the Great Lakes herring gull eggs, which may be linked to a TDBDPB source via ph

65 ed diphenoxybenzenes (MeO-PBDPBs) in herring gulls eggs from the Laurentian Great Lakes of North Amer

66 northern Alberta, California and Ring-billed Gulls exhibited statistically significant increases in e

67 n ECthreshold values were lower for CHSH and GULL extracts than for the other colonies.

68 In gulls, fast and coordinated reactions to predators may i

69 ury (MeHg) concentrations in glaucous-winged gull feathers from the Salish Sea.

70 ck of Hg trends over time in glaucous-winged gull feathers provides additional support that these gul

71 a(13)C, and delta(34)S declined over time in gull feathers.

72 These losses affected seals, eagles, sea gulls, fishes, and sea stars that depended on these prey

73 Most gulls flew off in response to the UAV, but returned to t

74 Shedding of mcr-1 E. coli by small gull flocks followed a lognormal curve and gulls shed on

75 Great black-backed gulls foraged primarily in marine habitats and herring g

76 ged primarily in marine habitats and herring gulls foraged primarily in specific urban habitats (e.g.

77 PB-DiPhOBz) contaminants reported in herring gulls from sites across the Laurentian Great Lakes.

78 Results indicate avian sources (i.e., gulls, geese) to be the largest nonpoint source of FIB a

79 Further, great black-backed gulls had significantly higher d(15)N and d(13)C than he

80 line EAC waters and crested terns and silver gulls had smaller foraging areas on days when more than

81 thers provides additional support that these gulls have decreased the amount of marine forage fish in

82 ining how much variation lesser black-backed gulls have in their migratory behaviour and examining wh

83 Urban-nesting populations of gulls have undergone rapid population increases worldwid

84 s were detected in poultry and a free-living gull in St.

85 l of 2015, H10N7 viruses were recovered from gulls in Iceland, and genomic analyses showed that the v

86 In 2015, we isolated four H10N7 viruses from gulls in Iceland.

87 3-9.8%), but peak prevalence in Black-headed Gulls in spring (4.2-13%).

88 fluenza viruses isolated from shorebirds and gulls in the Delaware Bay region and from ducks in Alber

89 Laughing Gulls, in particular, exhibited a significant (125%) inc

90 ults are consistent with the hypothesis that gulls increased terrestrial food inputs in response to d

91 days prior to gull control and absent during gull intervention, a significant reduction (p = 0.005).

92 hannel Shelter Island (CHSH, Lake Huron) and Gull Island (GULL, Lake Michigan) had among the highest

93 winged gull (L. glaucescens), and California gull (L. californicus)) from nesting sites across Canada

94 ing gull (Larus argentatus), glaucous-winged gull (L. glaucescens), and California gull (L. californi

95 ack-backed gulls (Larus marinus) and herring gulls (L. argentatus) in an urbanized area.

96 zil; Organon Teknika, Sao Paulo, Brazil; and Gull Laboratories, Salt Lake City, Utah) using a panel o

97 r Island (CHSH, Lake Huron) and Gull Island (GULL, Lake Michigan) had among the highest OHC burdens,

98 ds (glaucous gull Larus hyperboreus, Iceland gull Larus glaucoides, common murre Uria aalge and thick

99 taminated arctic top predators, the glaucous gull Larus hyperboreus from Svalbard.

100 -legged kittiwake Rissa tridactyla, glaucous gull Larus hyperboreus) sampled in 2008.

101 s of Arctic cliff-nesting seabirds (glaucous gull Larus hyperboreus, Iceland gull Larus glaucoides, c

102 y published data for income-breeding herring gulls Larus argentatus smithsonianus.

103 y published data for income-breeding herring gulls Larus argentatus smithsonianus.

104 f young godwit chicks, colonial short-billed gulls Larus brachyrhynchus.

105 Lesser black-backed gulls Larus fuscus are generalist seabirds that use a di

106 as investigated using harvested wild herring gull (Larus argentatus) and adult male Wister-Han rat li

107 three congeneric gull species (i.e., herring gull (Larus argentatus), glaucous-winged gull (L. glauce

108 us musculus), goat (Capra hircus), Audouin's gull (Larus audouinii), reindeer (Rangifer tarandus), gr

109 d Kittiwake (Rissa tridactyla), and Glaucous Gull (Larus hyperboreus).

110 erican populations of the Great Black-backed Gull (Larus marinus), a Holarctic species, from the Near

111 rds nesting on the Farallon Islands: western gull (Larus occidentalis), common murre (Uria aalge), Ca

112 es, from the Nearctic North American Herring Gull (Larus smithsonianus).

113 n a field study involving omnivorous herring gulls (Larus argentatus smithsonianus), egg AA isotopic

114 ocky island is a breeding colony for herring gulls (Larus argentatus) and great black-backed gulls (L

115 in six body compartments from female herring gulls (Larus argentatus; n=8) and the separate egg yolk

116 C) evidence from feathers of Glaucous-winged Gulls (Larus glaucescens) has shown that over the last 1

117 Glaucous-winged gulls (Larus glaucescens) have experienced a dietary shi

118 se and trophic ecology of great black-backed gulls (Larus marinus) and herring gulls (L. argentatus)

119 ls (Larus argentatus) and great black-backed gulls (Larus marinus), so I had a front-row seat to the

120 data of 12 urban-nesting lesser black-backed gulls, Larus fuscus, with habitat and behaviour data ove

121 The presence of non-H13 gull viruses in the gull-like lineage and of H13 gull viruses in other avian

122 HBCD concentrations in glaucous gull liver appeared relatively low when compared to OC c

123 For glaucous gull liver, annual median values of alpha-HBCD (1994-201

124 (BEHTBP) was detected in 89% of ring-billed gull livers (mean: 2.16 ng/g ww; max: 17.6 ng/g ww).

125 E-209 (57.2 +/- 12.2 ng/g ww) in ring-billed gull livers was unexpectedly high for this midtrophic gu

126 ruses in other avian lineages suggested that gulls' M genes do not preferentially associate with the

127 Exponential decay of gull marker in sand amended with live Catellicoccus mari

128 xceedances could be traced to gulls based on gull marker prevalence and correlations with FIB concent

129 ial-resistant bacteria for extended periods, gulls may facilitate transmission of mcr-1 positive E. c

130 Counts of gull nests and adults were similar between UAV and groun

131 Gulls occupied the lowest trophic level, with the widest

132 nd chicks are extremely vulnerable, and many gull offspring do not survive.

133 I once spent a summer studying gulls on Appledore Island in the Gulf of Maine, off the

134 a 90 min incubation period of solution 1 in gull or rat microsomal assays, there was no significant

135 from a ferret experiment demonstrated that a gull-origin H10N7 IAV replicated well in turbinate, trac

136 imilar to other avian-origin H10 IAVs, these gull-origin H10N7 IAVs bound to both avian-like alpha 2,

137 ave frequent contact with humans; therefore, gull-origin H10N7 IAVs could pose a risk to public healt

138 This gull-origin H10N7 virus can be transmitted between ferre

139 ion studies in ferrets demonstrated that the gull-origin IAV could infect ferrets, and that the virus

140 10N8 IAV, which caused human infections, the gull-origin virus showed significantly higher binding af

141 These gull-origin viruses showed high binding affinity to huma

142 However, when the gull-origin viruses were compared with another Eurasian

143 ective method of gull control: average daily gull populations fell from 665 before to 17 during inter

144 ndent circulation of H13 and H16 subtypes in gull populations, as antigenic patterns do not overlap,

145 ull densities when chicks are susceptible to gull predation but likely experience higher risk from al

146 cantly higher d(15)N and d(13)C than herring gulls, reflecting the use of marine, rather than urban,

147 Herring gull regurgitates and feces were collected from several

148 This study demonstrates that gull removal can be a highly successful beach remedial a

149 f four avian predators (snowy owls, glaucous gulls, rough-legged hawks and long-tailed jaegers) feedi

150 dants in wildlife, TBBPA-BDBPE levels in the gull samples were low with a few high values and increas

151 Gulls share their habitat with other birds and mammals a

152 l gull flocks followed a lognormal curve and gulls shed one strain >10(1) log10 CFU/g in their feces

153 opic evidence supporting the hypothesis that gulls shifted to terrestrial and/or freshwater prey.

154 monitoring of a breeding colony of Armenian Gulls showed that adult birds were seropositive on arriv

155 ears ago, an animal no bigger than a herring gull soared above shallow lagoons in what is now Bavaria

156 Now, when a gull soars past - or pilfers my sandwich at the beach -

157 r, MST revealed correlations between FIB and gull source tracking markers, leading to recommendations

158 samples for Bacteroides human, ruminant, and gull source-marker genes.

159 ings (Sturnus vulgaris) and three congeneric gull species (i.e., herring gull (Larus argentatus), gla

160 two zones of secondary contact between large gull species in Europe (Larus argentatus and Larus cachi

161 effect of living with stressed siblings in a gull species where, as in many vertebrates, family repre

162 We conclude that these large gull species, along with other recently diverged species

163 rs was unexpectedly high for this midtrophic gull species, exceeding levels reported in several apex

164 profiles typically reported for fish-eating gull species.

165 racemic for all annual mean EFs in glaucous gull suggesting metabolisation processes toward an enric

166 ined by a narrower host range, in particular gulls, than the majority of LPAIV subtypes and may there

167 hearwater, Mediterranean shag, and Audouin's gull, that die in different types of fishing gears: long

168 aker Toxocap-M, 100 and 95.9%, respectively; Gull Toxo IgM, 97 and 85.6%, respectively; and Sanofi Di

169 Realistic estimates of gull trophic position were obtained using bird Glu and P

170 Our study shows that gulls use their shoulder, wrist, and elbow joints to neg

171 of a best management practice (BMP) to abate gulls using a falconry program for the beach and an upla

172 The gulls utilised suburban and urban areas more as their ch

173 viruses in the gull-like lineage and of H13 gull viruses in other avian lineages suggested that gull

174 dian duck viruses and those of shorebird and gull viruses in the Delaware Bay shared ancestors with t

175 The presence of non-H13 gull viruses in the gull-like lineage and of H13 gull vi

176 ion results indicate that a 50% reduction in gulls was associated with a 38% and 29% decrease in Ente

177 effluent and, to a lesser extent, geese and gull wastes.

178 In this study, gulls were chased from a Lake Michigan beach using speci

179 tures such as central erosion, saw-tooth and gull-wing lesions and, rarely, ankylosis.

180 Warmer ocean temperatures in gulls' winter foraging areas in the North Sea were corre