527 research outputs found

    Evidence that Invasion by Cheatgrass Alters Soil Nitrogen Availability

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    Tetragonal CuO: A new end member of the 3d transition metal monoxides

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    Monoclinic CuO is anomalous both structurally as well as electronically in the 3dd transition metal oxide series. All the others have the cubic rock salt structure. Here we report the synthesis and electronic property determination of a tetragonal (elongated rock salt) form of CuO created using an epitaxial thin film deposition approach. In situ photoelectron spectroscopy suggests an enhanced charge transfer gap Δ\Delta with the overall bonding more ionic. As an end member of the 3d transition monoxides, its magnetic properties should be that of a high TNT_N antiferromagnet

    Influence of Plant Invasion on Seed Chemistry of Winterfat, Green Rabbitbrush, Freckled Milkvetch, Indian Ricegrass and Cheatgrass

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    Plant invasions have proven detrimental to numerous ecosystem processes; however, limited information exists on how plant invasions affect seed nutrients. We quantified nutrients in seeds of Indian ricegrass (Achnatherum hymenoides), green rabbitbrush (Chrysothamnus viscidiflorus), winterfat (Krascheninnikovia lanata), freckled milkvetch (Astragalus lentiginosus), and cheatgrass (Bromus tectorum) in sites invaded about 10 years by cheatgrass and in nearby sites with only widely scattered plants of cheatgrass. Seed chemistry differed significantly among the species tested. Overall, seeds of shrubs and freckled milkvetch had greater concentrations of N, P, and K, and lower C:N ratios than the grass species. On areas invaded by cheatgrass for 10 years, seeds trended towards decreased nutrients relative to seeds from non-invaded areas. Statistically, however, only winterfat, whose seeds from invaded areas had greater N and significantly lower C and C:N ratios, and cheatgrass, whose seeds from invaded areas had less P, were significantly different from non-invaded areas. Complimentary data suggests that cheatgrass invasion increases the availability of N, which explains an increase for seeds of winterfat; however, invasion also fosters high winterfat mortality. We suspect that high density of cheatgrass and cheatgrass litter on sites invaded for 10 years essentially ties-up large quantities of P, K and Mg, thus reducing amounts available for plant uptake. Overall, our data suggests declining nutritional value of seeds with plant invasion

    Effect of Atmospheric CO2 Levels on Nutrients in Cheatgrass Tissue

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    Rising atmospheric CO2 has resulted in declining tissue nutrient concentrations and leaf biochemicals, which has potential ramifications for animal nutrition, herbivory and litter decomposition rates. We investigated the interacting effects of atmospheric CO2 concentrations (270, 320, 370, and 420 ppmv), plant age (42, 57, 75, and 87 days), and elevation ecotype (salt desert, sagebrush steppe, and mountain brush) on aboveground tissue nutrient levels and biochemistry of cheatgrass (Bromus tectorum), an important range grass in the Great Basin. Most nutrients were affected by significant (P \u3c 0.05) interactions between CO2 level and plant age, and plant ecotype and plant age. At 87 days growth, tissue C:N ratios increased significantly and concentrations of P, K, and Mg declined, with rising CO2 levels suggesting declining forage nutrition. Tissue concentrations of Mn, K, Mg, and Ca increased with plant age and, in general, the low elevation ecotype had greater tissue nutrient concentrations than the high elevation ecotype. Hemicellulose concentration was influenced by a significant CO2 level by ecotype interaction; overall, the high elevation ecotype had greater concentrations of hemicellulose, which increased with increasing CO2 levels. The high elevation ecotype had significantly less acid detergent fiber than the low or mid elevation ecotypes. These data suggest that increasing atmospheric CO2 levels may have a profound effect on the nutritional value of cheatgrass forage, and this effect may differ among elevational ecotypes

    Quick Start Guide to Soil Methods for Ecologists

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    Increasingly biologists and ecologists are becoming aware of the vital importance of soil to processes observed above ground and are incorporating soil analyses into their research. Because of the dynamic and heterogeneous nature of soil, proper incorporation of soil analysis into ecological studies requires knowledge and planning. Unfortunately, many ecologists may not be current (or trained at all) in soil science.We provide this review, based on our cumulative \u3e60 years of work in soil science,to help familiarize researchers with essential information to appropriately incorporate soil analyses into ecological studies. Specifically, we provide a brief introduction into soils and then discuss issues related to soil sterilization, choosing a soil for a greenhouse project, sampling soils, and soil analyses

    Developing a Model Framework for Predicting Effects of Woody Expansion and Fire on Ecosystem Carbon and Nitrogen in a Pinyon-Juniper Woodland

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    Sagebrush-steppe ecosystems are one of the most threatened ecosystems in North America due to woodland expansion, wildfire, and exotic annual grass invasion. Some scientists and policy makers have suggested that woodland expansion will lead to increased carbon (C) storage on the landscape. To assess this potential we used data collected from a Joint Fire Sciences Program demonstration area to develop a Microsoft Excel™ based biomass, carbon, and nitrogen (N) spreadsheet model. The model uses input for tree cover, soil chemistry, soil physical properties, and vegetation chemistry to estimate biomass, carbon, and nitrogen accumulation on the landscape with woodland expansion. The model also estimates C and N losses associated with prescribed burning. On our study plots we estimate in treeless sagebrush-steppe ecosystems, biomass accounts for 4.5 Mg ha−1 C and 0.3 Mg ha−1 N this is \u3c10% of total estimated ecosystem C and N to a soil depth of 53 cm, but as tree cover increases to near closed canopy conditions aboveground biomass may account for 62 Mg ha−1 C and 0.6 Mg ha−1 N which is nearly 53% of total estimated ecosystem C and 13% of total estimated ecosystem N to a soil depth of 53 cm. Prescribed burning removes aboveground biomass, C and N, but may increase soil C at areal tree cover below 26%. The model serves as a tool by which we are able to assess our understanding of the system and identify knowledge gaps which exist for this ecosystem. We believe that further work is necessary to quantify herbaceous biomass, root biomass, woody debris decomposition, and soil C and N with woodland expansion and prescribed fire. It will also be necessary to appropriately scale these estimates from the plot to the landscape

    Influence of Prescribed Fire on Ecosystem Biomass, Carbon, and Nitrogen in a Pinyon Juniper Woodland

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    Increases in pinyon and juniper woodland cover associated with land-use history are suggested to provide offsets for carbon emissions in arid regions. However, the largest pools of carbon in arid landscapes are typically found in soils, and aboveground biomass cannot be considered long-term storage in fire-prone ecosystems. Also, the objectives of carbon storage may conflict with management for other ecosystem services and fuels reduction. Before appropriate decisions can be made it is necessary to understand the interactions between woodland expansion, management treatments, and carbon retention. We quantified effects of prescribed fire as a fuels reduction and ecosystem maintenance treatment on fuel loads, ecosystem carbon, and nitrogen in a pinyon–juniper woodland in the central Great Basin. We found that plots containing 30% tree cover averaged nearly 40 000 kg · ha−1 in total aboveground biomass, 80 000 kg · ha−1 in ecosystem carbon (C), and 5 000 kg · ha−1 in ecosystem nitrogen (N). Only 25% of ecosystem C and 5% of ecosystem N resided in aboveground biomass pools. Prescribed burning resulted in a 65% reduction in aboveground biomass, a 68% reduction in aboveground C, and a 78% reduction in aboveground N. No statistically significant change in soil or total ecosystem C or N occurred. Prescribed fire was effective at reducing fuels on the landscape and resulted in losses of C and N from aboveground biomass. However, the immediate and long-term effects of burning on soil and total ecosystem C and N is still unclear

    Woodland Expansion\u27s Influence on Belowground Carbon and Nitrogen in the Great Basin U.S.

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    Vegetation changes associated with climate shifts and anthropogenic disturbance can have major impacts on biogeochemical cycling and soils. Much of the Great Basin, U.S. is currently dominated by sagebrush (Artemisia tridentate (Rydb.) Boivin) ecosystems. Sagebrush ecosystems are increasingly influenced by pinyon (Pinus monophylla Torr. & Frém and Pinus edulis Engelm.) and juniper (Juniperus osteosperma Torr. and Juniperus occidentalis Hook.) expansion. Some scientists and policy makers believe that increasing woodland cover in the intermountain western U.S. offers the possibility of increased organic carbon (OC) storage on the landscape; however, little is currently known about the distribution of OC on these landscapes, or the role that nitrogen (N) plays in OC retention. We quantified the relationship between tree cover, belowground OC, and total below ground N in expansion woodlands at 13 sites in Utah, Oregon, Idaho, California, and Nevada, USA. One hundred and twenty nine soil cores were taken using a mechanically driven diamond tipped core drill to a depth of 90 cm. Soil, coarse fragments, and coarse roots were analyzed for OC and total N. Woodland expansion influenced the vertical distribution of root OC by increasing 15–30 cm root OC by 2.6 Mg ha−1 and root N by 0.04 Mg ha−1. Root OC and N increased through the entire profile by 3.8 and 0.06 Mg ha−1 respectively. Woodland expansion influenced the vertical distribution of soil OC by increasing surface soil (0–15 cm) OC by 2.2 Mg ha−1. Woodland expansion also caused a 1.3 Mg ha−1 decrease in coarse fragment associated OC from 75–90 cm. Our data suggests that woodland expansion into sagebrush ecosystems has limited potential to store additional belowground OC, and must be weighed against the risk of increased wildfire and exotic grass invasion
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