A central current debate in community ecology concerns the relative importance of deterministic versus stochastic processes underlying community structure. However, the concept of stochasticity presents several profound philosophical, theoretical and empirical challenges, which we address here. The philosophical argument that nothing in nature is truly stochastic can be met with the following operational concept of neutral stochasticity in community ecology: change in the composition of a community (i.e. community dynamics) is neutrally stochastic to the degree that individual demographic events -birth, death, immigration, emigration -which cause such changes occur at random with respect to species identities. Empirical methods for identifying the stochastic component of community dynamics or structure include null models and multivariate statistics on observational species-by-site data (with or without environmental or trait data), and experimental manipulations of 'stochastic' species colonization order or relative densities and frequencies of competing species. We identify the fundamental limitations of each method with respect to its ability to allow inferences about stochastic community processes. Critical future needs include greater precision in articulating the link between results and ecological inferences, a comprehensive theoretical assessment of the interpretation of statistical analyses of observational data, and experiments focusing on community size and on natural variation in species colonization order.
a b s t r a c tWe analyzed the evolution of red/orange flowers in four putatively bird-pollinated species of Macaronesian Lotus, with the aim of investigating whether this floral trait evolved from a similar trait found in some entomophilous Lotus species, namely the ability to modify flower color to red after anthesis. First, we mapped the ability to modify flower color in this group on a well-resolved and densely sampled phylogenetic tree of the Macaronesian Lotus. Secondly, we determined differences in light reflectance and pigment composition between petals of (1) prechange and postchange flowers in bee-pollinated species and (2) between bee and putatively bird-pollinated species. Post-anthesis flower color change evolved three times within Macaronesian Lotus, and putatively bird-pollinated species evolved within a clade with this ability to change flower color to red after anthesis. The evolutionary transition to red/orange flowers in the putatively bird-pollinated species involved biochemical changes similar to those of the developmental transition to red postchange flowers. In both cases there are changes in the composition of flavonols and anthocyanidins within the same metabolic pathways, especially in the cyanidin branch of pigment production, but not the activation or inactivation of additional branches of this pathway. Postanthesis color change in Lotus, from yellow to red, is thought to be an adaptation to reduce bee visits to already pollinated flowers. Our results are consistent with the hypothesis that constitutive red coloration for bird-pollination evolved from facultative red flower color change in Lotus. As red post-anthesis coloration is widespread in plants, this may possibly represent a widespread exaptive mechanism for the evolution of bird pollination.
G4G4G3G is the ancestral repeat-unit of horsetail MLG. Horsetail evolution was accompanied by quantitative and qualitative modification of MLG; variation within subgenus Hippochaete suggests that the structure and biosynthesis of MLG is evolutionarily plastic. Xyloglucan quantity correlates negatively with abundance of other hemicelluloses; but qualitatively, all monilophyte xyloglucans conform to a core pattern of repeat-unit sizes.
The
miniaturized optical emission spectrometry (OES) devices based
on various microplasma excitation sources provide reliable tools for
on-site analysis of heavy metal pollution, while the development of
convenient and efficient sample introduction approaches is essential
to improve their performances for field analysis. Herein, a small
activated carbon electrode tip is employed as solid support to preconcentrate
heavy metals in water and subsequently served as an inner electrode
of the coaxial dielectric barrier discharge (DBD) to generate microplasma.
In this case, heavy metal analytes in water are first adsorbed on
the surface of the activated carbon electrode tip via a simple liquid–solid
phase transformation during the sample loading process, and then,
fast released to produce OES during the DBD microplasma excitation
process. The corresponding OES signals are synchronously recorded
by a charge-coupled device (CCD) spectrometer for quantitative analysis.
This activated carbon electrode tip provides a new tool for sample
introduction into the DBD microplasma and facilitates “insert-and-go”
in subsequent DBD-OES analysis. With a multiplexed activated carbon
electrode tip array, a batch of water samples (50 mL) can be loaded
in parallel within 5 min. After drying the activated carbon electrode
tips for 5 min, the DBD-OES analysis is maintained at a rate of 6
s per sample. Under the optimized conditions, the detection limits
of 0.03 and 0.6 μg L–1 are obtained for Cd
and Pb, respectively. The accuracy and practicability of the present
DBD-OES system have been verified by measuring several certified reference
materials and real water samples. This analytical strategy not only
simplifies the sample pretreatment steps but also significantly improves
the sensitivity of the DBD-OES system for heavy metal detection. By
virtue of the advantages of high sensitivity, fast analysis speed,
simple operation, low cost, and favorable portability, the upgraded
DBD-OES system provides a more powerful tool for on-site analysis
of heavy metal pollution.
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