ライフサイエンスコーパス: gull

1 only slightly influenced total mortality in gulls.

2 eviously in eggs of wild Great Lakes herring gulls.

3 The gull abatement BMP was associated with improved beach wa

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

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

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

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

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

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

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

11 emperate radiations including the waterfowl, gulls and woodpeckers.

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

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

14 Gulls are often cited as important contributors of fecal

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

30 oportions of aquatic and terrestrial food in gull diets.

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

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

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

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

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

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

37 In gull eggs, the median summation operatorVMS concentratio

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

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

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

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

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

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

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

45 3-9.8%), but peak prevalence in Black-headed Gulls in spring (4.2-13%).

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

87 profiles typically reported for fish-eating gull species.

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

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

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

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

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

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

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

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

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

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

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