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1 edicting bioavailability of nanomaterials to aquatic plants.
2 a decrease of nanoparticle absorption by the aquatic plants.
3  and aquatic plants; or water, sediment, and aquatic plants.
4 ndance reducing light intensity reaching the aquatic plants.
5 s can assist "mate finding," particularly in aquatic plants.
6     Biomarkers reveal hominins had access to aquatic plants and protective woods in a patchwork lands
7 urnal cycles caused by the metabolism of the aquatic plants and shows stable and reproducible results
8 e nonfecal FIB source, beach wrack (decaying aquatic plants), and its impacts on water quality along
9  in northern Europe based on macrofossils of aquatic plants are in many cases ca. 2 degrees C warmer
10 ical microenvironments in the rhizosphere of aquatic plants at high spatiotemporal resolution with a
11 uenced nanomaterial bioavailability to three aquatic plants: Azolla caroliniana Willd, Egeria densa P
12 n and distribution of As was analyzed in the aquatic plant Ceratophyllum demersum to understand As me
13        To address this deficit we studied an aquatic plant community in an ecosystem subject to gradi
14                                     Vascular aquatic plant diversity may not necessarily enhance wetl
15 eciation and distribution was measured in an aquatic plant, duckweed (Landoltia punctata), exposed to
16 ment for studies of environmental impacts on aquatic plant ecophysiology.
17 d systematic processing of C3/C4 grasses and aquatic plants, gathered from the savannahs and lakes in
18  abandoned river channel with open water and aquatic plants; (ii) inundated forest swamp; and (iii) r
19 st in part, the neotenous reduction of these aquatic plants is based on readjusted copy numbers of pr
20 tems, but its influence on interactions with aquatic plants is still unclear.
21    All three silver treatments were toxic to aquatic plants, leading to a significant release of diss
22         We expressed human mAbs in the small aquatic plant Lemna minor, which offers several advantag
23 norhabditis elegans (nematode worm), and the aquatic plant Lemna minuta (least duckweed)).
24                          We demonstrate that aquatic plant macrofossil records can provide additional
25 ed the species richness of rooted, submerged aquatic plant (macrophyte) communities in experimental w
26 surface water; water and sediment; water and aquatic plants; or water, sediment, and aquatic plants.
27 with freshwater sediments and two species of aquatic plants (Potamogeton diversifolius and Egeria den
28 sequenced the transcriptome of the submerged aquatic plant Ranunculus bungei, and two terrestrial rel
29                       We used the decline in aquatic plant richness and cover as an index of ecologic
30 hydr)oxide rind, or Fe plaque, that forms on aquatic plant roots is an important sorbent of metal(loi
31 nal traits of native and nonnative submersed aquatic plants (SAP) in an aquatic ecosystem.
32                       In all terrestrial and aquatic plant species the primary cell wall is a dynamic
33 e sampling approach can be adopted for other aquatic plant systems.
34 ecies that have been sequenced and comprises aquatic plants that grow rapidly on the water surface.
35 nvestigate whether AFMK exists in plants, an aquatic plant, water hyacinth, was used.
36 us and Montsechia, open the possibility that aquatic plants were locally common at a very early stage

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