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Analyses of spatial interaction are to some degree plagued by uncertainty regarding the impact of spatially dispersed interaction masses within zones on travel times.
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This work may be of broad interest to those studying a variety of biological systems including protein folding, DNA-protein binding, and drug-receptor docking that depend on dispersed interactions.
It can be used as a carrier of transition metal in the nitrogen-containing complex catalysts, where the metal particles can be fixed on its surface and physically dispersed, the interaction between PPy and metal particles can work as efficient active site for ORR [20, 21].
Subsequently EhV can be carried and be potentially dispersed by interaction with zooplankton both via viral-dense fecal pellets or topical detachment.
The spatial scale at which plant-disperser interactions occur may determine the distribution, dynamics and genetic structure of plant populations and, therefore, of plant species assemblages [5] [7].
This may be particularly important within anthropogenic areas, where either the patchy distribution of wild plants or the presence of cultivated fleshy-fruits may influence plant-disperser interactions.
During the last decade, the spatial scale at which plant-disperser interactions are distributed have been addressed on different plant-frugivore systems, although mostly including birds [1], [2], [23], [24].
Carnivores greatly differ from birds in terms of feeding behaviour, mobility, gut retention time, habitat use and spatial patterns of seed deposition [20], [25], [27], which are pivotal features in determining the spatial scale of plant-disperser interactions.
Importance of interaction terms between fruit compounds and 'animal species' reveals the relevance of some animal phenotypic traits in determining fruit-disperser interactions, and suggests that different animal species might respond to fruit nutrients in different ways (Jordano 2000).
In this paper the authors take advantage of the simplicity of an insular community to evaluate the relative importance of species' phenotypic traits and species' abundance in determining fruit-avian disperser interactions, at both network and pairwise interaction levels.
The minimum value of n = 0.1 at < d > = 13.9(2) nm is known as a mono-dispersed interaction.
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