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1 strategic habitats (e.g., mosquito-infested swamps).
2 ebrate community diversity, in Cuba's Zapata Swamp.
3 n that was originally interpreted as a muddy swamp.
4 d with distance from the stream inlet to the swamp.
5 as diminished by 25-30% in short-hydroperiod swamps.
6 Ma) natural levees, back swamps, and coastal swamps.
7 outliers despite the effects of masking and swamping.
8 appeared to buffer this effect through prey swamping.
9 ream as compared to the upstream half of the swamp (0.66 and 1.34 ng MeHg g(-)(1) SOC(-)(1) annual av
11 lobal wetlands), comprising 46% marshes, 25% swamps, 22% peatlands, 5% seasonal wetlands, and 2% mang
12 xamine the same four Willandra Lakes and Kow Swamp 8 (KS8) remains studied in the work by Adcock et a
13 dissolved organic carbon (DOC) from mangrove swamps accounts for 10% of the global terrestrial flux o
15 ent physiological strategies, with deciduous swamp-adapted genera-like Taxodium at one extreme, and e
17 op climate change is not an answer-this will swamp all adverse impacts of even unjust mitigation in t
18 accumulation in some inundated tropical peat swamps, although this can lead ultimately to a shift to
23 number of water sites, and type (beach/pond/swamp), and lower village-level infection prevalence.
24 story floodplains (excluding levees and back swamps); and (iii) Cenomanian-Campanian (ca. 100-84 Ma)
27 at Vasyugan mire, which is the world largest swamp, and receives huge load of the Irtysh waters which
28 gest that MeHg was net degraded in the Alnus swamp, and that it had a rapid and dynamic internal turn
30 er and aquatic plants; (ii) inundated forest swamp; and (iii) raised peat dome (since ca. 3.9 ka BP).
33 w that the peatland originated as a mangrove swamp beginning >7,700 years before present (BP) and Sph
36 e distance of the subject's residence from a swamp bordering the parish showed a strong "dose-respons
39 's buffalo are genetically closer to Chinese swamp buffalo populations than those from South Asia, su
40 alo haplotype detected in one phenotypically swamp buffalo suggests introgression from Murrah buffalo
41 sive statewide genetic assessment of Sabahan swamp buffalo using mitochondrial cytochrome b (cytb) ge
42 ed maternal genetic variation within Sabahan swamp buffalo, likely stemming from a founder effect dur
43 history and population structure of Sabah's swamp buffalo, with implications for conservation and li
44 s, however, global environmental changes are swamped by dramatic changes in the local environment.
47 , when the environment varies across space, "swamping" by gene flow creates a positive feedback betwe
48 ts, pechay (bok choy), squash, and kangkong (swamp cabbage)] and 7, 15, or 29 g fat/d (2.4, 5, or 10
49 into glucose, to minimize the risk of loads swamping capacities, to handle suddenly increased nutrie
53 the feeding dynamics of a population of red swamp crayfish in Lake Naivasha, Kenya, after the crash
54 d further highlight the traits that make red swamp crayfish such opportunistic and successful invader
56 redwood (Metasequoia glyptostroboides), and swamp cypress (Taxodium distichum) at an elevated pCO2 o
58 t or weak selection are likely to be lost by swamping during secondary contact, even when selection a
61 es indicate that invasion of predatory Asian Swamp Eels (Monopterus albus/javanensis) has disrupted t
67 These findings show that exogenous THC can swamp endogenous anandamide signaling systems, thereby a
68 iments were deposited in a coastal-estuarine swamp environment at the outlet of a >1500-km-long trans
72 orded protection from predation via predator swamping, experiencing reduced per-capita encounter risk
73 ng the possibility of sustainability of peat swamp exploitation via drainage-based agriculture throug
74 these Neolithic communities selected lowland swamps for their rice cultivation and settlement, using
75 We carried out field research in a Malaysian swamp forest and an oil palm plantation to understand ho
76 fluvial organic carbon from both intact peat swamp forest and peat swamp forest subject to past anthr
78 dissolved organic carbon from disturbed peat swamp forest consists mostly of much older (centuries to
79 simulated carbon loss caused by coastal peat swamp forest conversion into oil palm plantation with pe
80 nge between the atmosphere and tropical peat swamp forest in Sarawak, Malaysia using the eddy covaria
82 nal net CO(2) losses from this tropical peat swamp forest in the absence of plant acclimation to such
83 vial organic carbon flux from disturbed peat swamp forest is about 50 per cent larger than that from
84 gest that conversion of Southeast Asian peat swamp forest is contributing between 16.6 and 27.9% (95%
85 of dissolved organic carbon from intact peat swamp forest is derived mainly from recent primary produ
86 te that emissions factors for converted peat swamp forest is in the range 70-117 t CO(2) eq ha(-1) yr
87 how that flammability and decomposability of swamp forest leaves are decoupled because flammability i
88 nalysed waters from intact and degraded peat swamp forest of Kalimantan, Indonesian Borneo, and an oi
89 gged condition, peat and water overlying the swamp forest on average emits 11.02 +/- 0.49 MgCO(2) ha(
90 peatlands support a luxuriant growth of peat swamp forest overlying peat deposits up to 20 metres thi
92 from both intact peat swamp forest and peat swamp forest subject to past anthropogenic disturbance.
95 GHGs emitted during the conversion from peat swamp forest to oil palm plantation, accounting for CH(4
96 We find extensive peat deposits beneath the swamp forest vegetation (peat defined as material with a
97 O(2) efflux from the recently-burnt, cleared swamp forest was as old as from the oil palm plantation.
98 fluvial organic carbon export over the peat swamp forest within an undrained tropical peatland lands
99 es were a N(2)O source (except for inundated swamp forest) with 0.93, 1.56, 3.5, and -0.19 kg N(2)O-N
100 ry to wet seasons), in a palm-dominated peat swamp forest, a hardwood-dominated peat swamp forest, an
102 one of the world's most extensive regions of swamp forest, the Cuvette Centrale depression in the cen
105 Drainage and deforestation of tropical peat swamp forests (PSF) in Southeast Asia cause carbon emiss
112 both more common and diverse - preserved in swamp forests with modes of attachment ranging from aeri
113 before the demise of Pennsylvanian age coal-swamp forests, a highly stereotyped life cycle was alrea
114 for temperate wet forests and tropical peat swamp forests, representing the largest non-ebullitive w
116 d to key plant functional traits in tropical swamp forests, where habitat degradation is elevating de
125 hough Hg and MeHg yields from tidal mangrove swamps have not been previously measured, our estimated
127 010 revealed a black alder (Alnus glutinosa) swamp in southern Sweden to be a consistent and signific
128 osphere from a permanent, vegetated tropical swamp in the Okavango Delta, Botswana, and we find that
130 urements at eight additional Alnus glutinosa swamps in southern Sweden indicate that Alnus swamps in
131 ravene the long-held assumption that genetic swamping is a common driver of species range limits, and
133 and suggest that restored or preserved Alnus swamps may be used to mitigate MeHg produced in northern
134 plateau, with the exception that OCD in the swamp meadow was substantially higher than that in surro
135 inity gradient (SG), as observed in mangrove swamps (MSPs), influence their aggregation pathways.
138 at least semiaquatic and lived in freshwater swamp or riverine environments, where they grazed on fre
139 his population spread to Eurasia, where they swamped or replaced the Neanderthals and other nonmodern
141 line, or human land use and disturbance, may swamp out any signal of climate-mediated migration in th
143 sparsity helps prevent sampling errors from swamping out the true signal in high-dimensional data.
144 stem state shifts (open water wetland-forest swamp-peat dome) suggests a potential climatic control o
145 y stall or aid adaptation at range limits by swamping peripheral populations with maladaptive gene fl
146 deserts) or higher access to fast food (food swamps) reduces healthy food access and has been underst
149 ounties or county equivalents with high food swamp scores (adjusted odds ratio, 1.77; 95% CI, 1.43-2.
150 nship among 3 levels of food desert and food swamp scores and obesity-related cancer mortality was al
151 for the association of food desert and food swamp scores with obesity-related cancer mortality rates
152 bog-fen peatland gradient and a black alder swamp, serving as net sources and a sink for methylmercu
155 eport that a certain class of neurons in the swamp sparrow forebrain displays a precise auditory-voca
157 Here we examine song type representations in swamp sparrows (Melospiza georgiana), a multiple song ty
159 dual sensorimotor neurons in freely behaving swamp sparrows expressed categorical auditory responses
161 y studying neural representations of song in swamp sparrows, a species in which juveniles learn and p
163 that noise within the auditory system would swamp such tiny motions, making weak sounds imperceptibl
164 ore efficiently in the peatlands than in the swamp, suggesting an increasing role of sulfate-reducing
165 g as overwintering areas while nearby inland swamps support significant breeding in spring, summer, a
166 nfluenced microbiome composition but did not swamp the dominant signal of host genetic background.
168 e sensitive to host processes that starve or swamp the prokaryote with large fluctuations in local zi
169 n of strongly deleterious or lethal alleles, swamping the effect of any potentially adaptive alleles
170 in transport were a saturable process, then "swamping" the capillary endothelial insulin receptors wi
173 iving the impression that the mesoscale is a swamp to be crossed without getting mud on our boots.
174 ging from pH 3.5 in peatlands and freshwater swamps to pH 9.0 in soda lakes and freshwater marshes) a
177 ze grows, truncation-induced bias eventually swamps variance, rendering nominal confidence interval c
181 "dose-response" relationship; living in the swamp was the strongest predictor of malaria risk (RR, 3
184 on, this epidemic was focused near lakes and swamps, where it was associated with high infection and
185 s and eight genera restricted to floodplain, swamp, white-sand or plateau forests of Central Amazonia