Do Tree Canopies Enhance Perennial Grass Restoration in California Oak Savannas?

Scattered trees in grass‐dominated ecosystems often act as islands of fertility with important influences on community structure. Despite the potential for these islands to be useful in restoring degraded rangelands, they can also serve as sites for the establishment of fast growing non‐native species. In California oak savannas, native perennial grasses are rare beneath isolated oaks and non‐native annual grasses dominate. To understand the mechanisms generating this pattern, and the potential for restoration of native grasses under oaks, we asked: what are the effects of the tree understory environment, the abundance of a dominant non‐native annual grass (Bromus diandrus), and soils beneath the trees on survival, growth, and reproduction of native perennial grass seedlings? We found oak canopies had a strong positive effect on survival of Stipa pulchra and Poa secunda. Growth and reproduction was enhanced by the canopy for Poa but negatively impacted for Stipa. We also found that Bromus suppressed growth and reproduction in Stipa and Poa, although less so for Stipa. These results suggest the oak understory may enhance survival of restored native perennial grass seedlings. The presence of exotic grasses can also suppress growth of native grasses, although only weakly for Stipa. The current limitation of native grasses to outside the canopy edge is potentially the result of interference from annual grasses under oaks, especially for short‐statured grasses like Poa. Therefore, control of non‐native annual grasses under tree canopies will enhance the establishment of S. pulchra and P. secunda when planted in California oak savannas.     

Bulking generated considerable bias in detection of amplified fragment length polymorphism variations in oat,fringed brome and smooth bromegrass

Amplified fragment length polymorphism (AFLP) variations in bulk and plant‐by‐plant (PBP) samples of five oat (Avena sativa L.) accessions, one fringed brome (Bromus ciliatus L.) accession and two smooth bromegrass (B. inermis Leyss.) accessions were compared. The proportions of AFLP bands detected in PBP, but lost in bulk, samples of oat, fringed brome, and smooth bromegrass ranged from 19 to 31%, 40 to 44%, and 22 to 33% of the total bands scored, respectively. These lost bands had occurred at frequencies ranging from 0.1 to 1 in the PBP samples. These findings demonstrate bulking can generate substantial bias in detection of AFLP variations.     

无籽刺梨多糖纳米粒制备工艺优化及表征

目的:采用双乳化溶剂蒸发法,优化无籽刺梨多糖纳米粒制备工艺,并对其进行表征.方法:采用响应面法以内水相W1和有机相O的比例、初级乳PE和外水相W2的比例以及泊洛沙姆P188的浓度为自变量,纳米粒的包封率为响应值,对制备工艺进行优化.结果:最佳制备工艺为W1和O的比例为1:8,PE和W2的比例为1:7,泊洛沙姆P188的...     

Maternal and direct effects of elevated CO2 on seed provisioning, germination and seedling growth in Bromus erectus

Elevated CO₂ can affect plant fitness not only through its effects on seed production but also by altering the quality of seeds and therefore germination and seedling performance. We collected seeds from mother plants of Bromus erectus grown in field plots at ambient and elevated CO₂ (m-CO₂, maternal CO₂) and germinated them in the greenhouse in a reciprocal design under ambient and elevated CO₂ (o-CO₂, offspring CO₂). This design allowed us to examine both the direct effects of elevated CO₂ on germination and seedling growth and the indirect (maternal) effects via altered seed quality. Elevated m-CO₂ significantly increased seed mass and increased the C:N ratio of seeds from field-grown plants. Percentage and rate of germination were not affected by the m-CO₂ or o-CO₂ treatments. Similarly, elevated m-CO₂ had no significant effect on seedling size as estimated by the total leaf length. When differences in seed mass were adjusted by using seed mass as a covariate in ANOVA, a negative effect of m-CO₂ on seedling size appeared which increased with increasing seed mass (significant covariate×m-CO₂ interaction). This may indicate that the advantage of increased seed mass at elevated m-CO₂ was offset by the reduced concentration of nitrogen (and possibly other nutrients) in these seeds. In contrast to m-CO₂, elevated o-CO₂ greatly increased seedling size, and this stimulatory effect of elevated o-CO₂ was found to increase with increasing seed mass (significant covariate×o-CO₂ interaction). Taken together, these results suggest that in B. erectus transgenerational effects of elevated CO₂ are relatively small. However, other factors (genetic and environmental) that contribute to variation in seed provisioning can critically influence the responsiveness of seedlings to elevated CO₂. Received: 10 May 1999 / Accepted: 6 January 2000     

Determinants of plant community composition of remnant biancane badlands: a hierarchical approach to quantify species‐environment relationships

Question: Which environmental variables best explain patterns in the vegetation of biancane badlands? What is the role of spatial scales in structuring the vegetation of biancane badlands within the agricultural matrix? Location: Five biancane badlands in Central Italy (Tuscany). Methods: An object‐oriented approach on high‐resolution multispectral images was used to classify physiognomic vegetation types in five biancane badlands. Within each badland, data on vascular plant species abundance were collected using a stratified random design. Variation partitioning based on partial redundancy analysis was used to evaluate the contribution of three sets of environmental predictors, recorded at the spatial scales of plot, patch and biancane badland in explaining patterns in plant community composition. Results: Environmental variables included in the final model – electrical conductivity and carbon/nitrogen ratio (plot scale), shape index (patch scale) and area (biancane badland scale) – accounted for 15.5% of the total variation in plant community composition. Soil characteristics measured at the plot level explained the majority of variation. In the smallest badlands, Bromus erectus perennial grasslands were absent, while annual grasslands, linked with harsh soil conditions (i.e. high soil salinity), were not affected by either the surface area of biancane badlands or by the soil nitrogen availability. Conclusions: The identification of the major predictors of patterns in remnant vegetation requires conducting investigations at multiple spatial scale. Management strategies should operate at different spatial scale, preventing any further reduction in the size of existing badlands and relying on habitat‐ instead of area‐focused conservation practices.     

Eco‐evolutionary responses of Bromus tectorum to climate change: implications for biological invasions

How plant populations, communities, and ecosystems respond to climate change is a critical focus in ecology today. The responses of introduced species may be especially rapid. Current models that incorporate temperature and precipitation suggest that future Bromus tectorum invasion risk is low for the Colorado Plateau. With a field warming experiment at two sites in southeastern Utah, we tested this prediction over 4 years, measuring B. tectorum phenology, biomass, and reproduction. In a complimentary greenhouse study, we assessed whether changes in field B. tectorum biomass and reproductive output influence offspring performance. We found that following a wet winter and early spring, the timing of spring growth initiation, flowering, and summer senescence all advanced in warmed plots at both field sites and the shift in phenology was progressively larger with greater warming. Earlier green‐up and development was associated with increases in B. tectorum biomass and reproductive output, likely due early spring growth, when soil moisture was not limiting, and a lengthened growing season. Seeds collected from plants grown in warmed plots had higher biomass and germination rates and lower mortality than seeds from ambient plots. However, in the following two dry years, we observed no differences in phenology between warmed and ambient plots. In addition, warming had a generally negative effect on B. tectorum biomass and reproduction in dry years and this negative effect was significant in the plots that received the highest warming treatment. In contrast to models that predict negative responses of B. tectorum to warmer climate on the Colorado Plateau, the effects of warming were more nuanced, relied on background climate, and differed between the two field sites. Our results highlight the importance of considering the interacting effects of temperature, precipitation, and site‐specific characteristics such as soil texture, on plant demography and have direct implications for B. tectorum invasion dynamics on the Colorado Plateau.