ライフサイエンスコーパス: marine food web

1 hic-level fisheries expand ("fishing through marine food webs").

2 f the potent neurotoxin methylmercury in the marine food web.

3 litate entry of T. gondii into the nearshore marine food web.

4 ynthesis, changing energy fluxes through the marine food web.

5 ic organisms and are major components of the marine food web.

6 an readily pass from the water column to the marine food web.

7 als, thus "fishing-down" this element of the marine food web.

8 g uptake and trophic transfer at the base of marine food webs.

9 non-consumptive effects of top predators in marine food webs.

10 lankton dynamics, biogeochemical cycles, and marine food webs.

11 communities, with cascading consequences for marine food webs.

12 primary production and form the base of many marine food webs.

13 valence of undiscovered HOCs accumulating in marine food webs.

14 is important to understanding its entry into marine food webs.

15 l mercury and subsequently bioaccumulated in marine food webs.

16 thotrophy and organic matter assimilation in marine food webs.

17 bioaccumulation and trophic transfer through marine food webs.

18 that biomagnify into upper trophic levels of marine food webs.

19 ffected by processes at the bottom of Arctic marine food webs.

20 ich marks the entry of mercury into northern marine food webs.

21 basis of some of the world's most productive marine food webs.

22 matic predators that play a key role in most marine food webs.

23 itat is a major entry point for mercury into marine food webs.

24 ter basic nutrient and carbon fluxes through marine food webs.

25 sight on how future climate change can alter marine food webs.

26 n and constitute a vital trophic link within marine food webs.

27 vity that regulate the flux of carbon across marine food webs [1-3].

28 kton communities, which form the base of the marine food web and are a crucial element of the carbon

29 biological uptake at the base of the Arctic marine food web and may explain the elevated MeHg concen

30 a noteworthy route by which petroleum enters marine food webs and a previously overlooked biological

31 Here, we explore protistan trophic modes in marine food webs and broader biogeochemical influences.

32 This could alter productivity, marine food webs and carbon sequestration in the Arctic

33 magnitude of phytoplankton blooms that fuel marine food webs and influence global biogeochemical cyc

34 n that accumulates in predominantly tropical marine food webs and leads to ciguatera fish poisoning.

35 centrations of this toxic mercury species in marine food webs and seafood.

36 y production exerts a fundamental control on marine food webs and the flux of carbon into the deep oc

37 a large influence on the future stability of marine food webs and the functioning of global biogeoche

38 ining when predators collapse ("fishing down marine food webs") and when low-trophic-level fisheries

39 PUAs) are bioactive on various levels of the marine food web, and yet the potential for these molecul

40 Mercury is a widespread contaminant in marine food webs, and identifying uptake pathways of mer

41 Marine food webs are the most important link between the

42 iability provides information on function of marine food webs, biogeochemical cycles and copepod heal

43 y have played key roles in the regulation of marine food webs, biogeochemical cycles, and Earth's cli

44 ocean pH, with potentially severe impacts on marine food webs, but empirical data documenting ocean p

45 ries in the world but also play key roles in marine food webs by transferring energy from plankton to

46 ton primary production is at the base of the marine food web; changes in primary production have dire

47 uce PCB pollution, their biomagnification in marine food webs continues to cause severe impacts among

48 e world's oceans in recent decades, altering marine food webs, habitats and biogeochemical processes

49 Numerical simulations use a marine food web in Alaska to illustrate the model and to

50 he Cumberland Sound (Nunavut, Canada) arctic marine food web in the presence of transient species usi

51 an readily pass from the water column to the marine food web in three laboratory-constructed estuarin

52 the food web, increasing risk throughout the marine food web, including humans.

53 at effect this has on arsenic cycling within marine food webs is essential to clarify the role of the

54 nitial magnitude of MMHg uptake into pelagic marine food webs is influenced by the degree of primary

55 anic matter on the trophodynamics of coastal marine food webs is not well understood.

56 The potential of predation to structure marine food webs is widely acknowledged.

57 Contaminant dynamics in arctic marine food webs may be impacted by current climate-indu

58 mple food chains, transfer to a more complex marine food web model in which cascades are induced by v

59 We use a realistic marine food-web model, resolving species over five troph

60 ally less newsworthy - they are the basis of marine food webs, supporting fisheries and charismatic m

61 Tunas are apex predators in marine food webs that can accumulate mercury (Hg) to hig

62 , but despite their vital ecological role in marine food-webs, the impact of microplastics on zooplan

63 pheric Hg loading have rapidly propagated up marine food webs to a commercially important species.

64 , thereby, have far reaching consequences on marine food webs unless safeguards are in place to avoid

65 Using 23 large marine food webs, we show that food web responses to inc

66 Thus terrestrial-derived subsidies in marine food webs were primarily composed of young organi

67 ance, and thus biomass, near the base of the marine food web with potentially significant feedback ef

68 Photosynthesis fuels marine food webs, yet differences in fish catch across g