Soil Physical, Microbial Enzyme, and Molecular Characterization of Native Prairie and Agricultural Ecosystems S.H. Anderson, R.J. Kremer, and N. Mungai.

Slides:



Advertisements
Similar presentations
Do In and Post-Season Plant-Based Measurements Predict Corn Performance and/ or Residual Soil Nitrate? Patrick J. Forrestal, R. Kratochvil, J.J Meisinger.
Advertisements

Peter Motavalli, Javier Aguilera, Roberto Miranda, Jorge Cusicanqui, Miguel Angel Gonzales, Carola Chambilla, Mirco Peñaranda, and Edwin Yucra Students:
Assessing Soil Health in Missouri Agricultural Soils Kristen Veum Robert Kremer Keith Goyne Soil Health Workshop. Bradford Extension and Research Center.
Nitrogen Mineralization Across an Atmospheric Nitrogen Deposition Gradient in Southern California Deserts Leela E. Rao 1, David R. Parker 1, Andrzej Bytnerowicz.
Cover Crops and Biofuels Implications for Soil Characteristics and Plant Development Deanna Boardman October 21, 2009.
Soil and Water Quality with Miscanthus on a Louisiana Coastal Plain Hillside L. Gaston and W. Felicien LSU AgCenter School of Plant, Environmental and.
SOIL QUALITY ASSESSMENT
Characterization of Soil Resilience as influenced by Organic Management Practices in Perturbed Vertisol Ritesh Saha ICAR- Indian Institute of Soil Science.
Walker River Basin Project Water PlantSoil Interactions Interactions.
Yaron Fireizen, Vinay Rao, Lacy Loos, Nathan Butler, Dr. Julie Anderson, Dr. Evan Weiher ▪ Biology Department ▪ University of Wisconsin-Eau Claire From.
MICROBIAL DYNAMICS IN CONVENTIONAL AND ORGANIC MANAGED SYSTEMS LACHNICHT WEYERS, S.L., ARCHER, D.A., JOHNSON, J., WILTS, A., BARBOUR, N., AND EKLUND, J.
Chapter 4: Soil Architecture and Physical Properties
Soil Physical Properties Used to Assess Soil Quality Field Exercise.
Ch. 4 continued Soil Properties.
Tshepiso Seobi Graduate Adviser: Dr. Stephen Anderson
Impact of Soil Health on Crop Production Francisco J. Arriaga Soil Science Specialist Dept. of Soil Science & UW-Extension.
Measuring Soil Physical Properties to Assess Soil Quality Charles W. Raczkowski North Carolina A&T State University Presented at the Soil Quality Workshop.
Dust Generator To compare DG (Fig 6) estimates to wind tunnel measured dust emissions, the GRIMM spectrometer output from the tunnel was analyzed against.
Drivers of Soybean Rhizobia Diversity in Un-inoculated Soils of Smallholder Farms in Malawi. Parr M 1, Shumba L 2, Snapp S 3, and Grossman J Department.
Soil biological indicators: Organic Farming Systems Dr. Rachel Creamer, Prof. Bryan Griffiths Johnstown Castle Environment Research Centre Acknowledgements:
Residue Biomass Removal and Potential Impact on Production and Environmental Quality Mahdi Al-Kaisi, Associate Professor Jose Guzman, Research Assistant.
Integrating Forages into Multi-Functional Landscapes: Enhanced Soil Health and Ecosystem Service Opportunities Douglas L. Karlen USDA-ARS Presented at.
Effects of land use on soil microbial communities in the Cerrado region 1 Silva, M. R. S. S., 1 Bresolin, J. D., 2 Krüger, R. H., 1 Bustamante, M. M. C.,
GEOG 1113: Landform Geography Lecture 1: Soils Earth’s Internal Structure.
Assessing Soil Quality for Sustainable Agricultural Systems in Tropical Countries Using Spectroscopic Methods B. Jintaridth 1, P.P. Motavalli 1, K.W. Goyne.
Cornell University 2009 ASA-CSSA-SSSA Meetings High C/N ratio Refugia pH & aeration Physico- chemical sorption Surface change Microbes Nutrients Amending.
INTRODUCTION Poultry litter (PL) is a combination of poultry manure and bedding materials (e.g. pine shavings, saw dust, or peanut hulls). It also varies.
Surface Cover and Biomass in No-tillage Cropping Systems as Affected by Crop Rotation, Winter Cover Crop, and Winter Weeds Forbes Walker 1, Nick Ryan 1,
SOIL CONDITION INDEX – (SCI) AS AN INDICATOR OF THE SOIL ORGANIC MATTER DYNAMICS AT THE FARM BUTMIR NEAR SARAJEVO Prof. Dr. Hamid Čustović Tvica Mirza.
Peter Motavalli Dept. of Soil, Environmental and Atmos. Sci. University of Missouri University of Missouri ADAPTING TO CHANGE:
Background Deriving fuel from biological sources is an idea that has become popular as fossil fuel supplies are diminished, atmospheric carbon dioxide.
INFLUENCE OF LANDUSE ON ORGANIC MATTER DISTRIBUTION IN SOIL AGGREGATE SIZE FRACTIONS IN ILE-IFE, SOUTHWESTERN NIGERIA By Oyedele, D.J.; Pini, R.; Sparvolli,
Approach: Samples were obtained from 4 different plots of land, each with a different land-use. The land uses that were examined were a grassland (hayed),
Results of Long-Term Experiments With Conservation Tillage in Austria Introduction On-site and off-site damages of soil erosion cause serious problems.
Trace that Nitrate An Overview of “Nitrate Stable Isotopes: Tools for Determining Nitrate Sources Among Different Land Uses in the Mississippi Basin” by.
Consequences of Aluminum or Ferrous Sulfate Amended Poultry Litter on Concentrations of Aluminum in Plant and Soil Sosten Lungu, Haile Tewolde and Dennis.
The diagnostic features used to differentiate soils in USDA Soil Taxonomy are primarily macromorphological Soils can also be studied at smaller scales.
Water Movement Below Surface
Soil Water Tension Department of Agricultural and Biological Engineering University of Illinois at Urbana-Champaign.
Figure 1. Residue removal effects on corn yields as affected by N rate in 2009 and 2010 for poorly and well-drained soils. Asterisk indicates significant.
Application of Differential Scanning Calorimetry to Determine Enthaplic Character of Composts, Dissolved Organic Carbon (DOC) and Soils Julie Bower, Garrett.
DRAINMOD APPLICATION ABE 527 Computer Models in Environmental and Natural Resources.
Microbial biomass and community composition of a tallgrass prairie soil subjected to simulated global warming and clipping A. Belay-Tedla, M. Elshahed,
Soil Carbon and Phosphorous Fractions in Ciampitti I.A. 123, F.O. García 1, G. Rubio 2 and L.I. Picone 4 Field Crop Rotations of the Argentine Pampas Ciampitti.
Figure 3. Concentration of NO3 N in soil water at 1.5 m depth. Evaluation of Best Management Practices on N Dynamics for a North China Plain C. Hu 1, J.A.
Mixed Oak Ecosystem: Field and Lab Data Integration Deborah Hudleston Catherine Resler Mary Walton Chris Weber.
Introduction to Biological Concepts and Research Chapter 1.
Diversity of Soil Microbes. Approaches for Assessing Diversity Microbial community Organism isolation Culture Nucleic acid extraction Molecular characterization.
Comparison of Soils and Plants at Prairie Ridge: % C and % N Lori Skidmore.
 Types of STR markers- 5 types based on sequence  STR allele nomenclature  Allelic ladder  Serological methods of identity profiling  Identity profiling.
STUBBLE BURNING AND TILLAGE EFFECTS ON SOIL ORGANIC C, TOTAL N AND AGGREGATION IN NORTHEASTERN SASKATCHEWAN S. S. Malhi 1 and H. R. Kutcher 1 1 Agriculture.
Influence of Nitrogen Sources and Soil pH on Soil Microbial Communities in a Long-term Crop Rotation System Reji Mathew, Yucheng Feng, and Charles Mitchell.
Effects of Prairie Management on Soil Characteristics and Bees METHODS RESULTS  Soil Characteristics Analysis of variance (ANOVA) suggests that there.
Use of Slow Release Nitrogen Fertilizer and its effect on soil quality. Soil bacterial population Hernandez, Jorge D., Garcia, Rosalia. and Lightfoot,
CORRELATION BETWEEN HYDROLOGICAL, GEOCHEMICAL AND MICROBIOLOGICAL PROCESSES IN GROUNDWATER-STREAM WATER MIXING ZONE Heejung Kim, Seong-Sun Lee, Yunjung.
Wood ash, the residue remaining from the combustion of bark, sawdust and yard waste for energy generation for forestry product operations, is an effective.
Results and Discussion Conclusions and Suggestions
Y. Ikemura1, P. A. Jacinthe3 and M. K. Shukla2
Soil Physical Properties Used to Assess Soil Quality
Soil Bulk Density/Moisture/Aeration
Mechanistic modeling of microbial interactions at pore to profile scales resolve methane emission dynamics from permafrost soil Ali Ebrahimi and Dani Or.
Figure 5. Do not be afraid to leave plenty of white space around your figures. If you use someone else’s figure, always acknowledge the source. Figures.
Results and Discussion
NDVI Active Sensors in Sugarbeet Production for In-Season and Whole Rotation Nitrogen Management.
Carbon Cycling in Perennial Biofuel Management Systems
Topsoil Depth at the Centralia Site
Department of Agriculture & Environmental Science, Lincoln University
Management and Life Cycle Assessment of Bioenergy Crop Production
Soils 5.02: Discuss the soil profile and soil sampling for surface and subsurface layers.
Long-term crop rotations suppress soybean sudden death
Presentation transcript:

Soil Physical, Microbial Enzyme, and Molecular Characterization of Native Prairie and Agricultural Ecosystems S.H. Anderson, R.J. Kremer, and N. Mungai Department of Soil, Environmental & Atmospheric Sciences, University of Missouri USDA-ARS Cropping Systems and Water Quality Research Unit, Columbia, Missouri Materials and Methods (cont.)  Additional soil samples were taken and essayed for energy transformation enzymes (dehyrogenase); nutrient mineralization enzymes for C (β- glucosidase), P (alkaline phosphatases), and N (β- glucosamidase); soil microbial diversity by a C substrate utilization assay; and CO 2 respiration.  Total soil DNA was extracted, quantified, and subjected to amplification (polymerase chain reaction, PCR) with known, primer DNA to detect various bacterial genotypes. Different DNA sequence combinations resulting from PCR were separated on a gel matrix using electrophoresis, visualized as a series of bands distributed over the matrix. The series of bands obtained from separating the DNA fragments resulted in genetic profiles that characterized microbial communities. Results  Soil bulk density was 32% lower for the native prairie site (TP) compared to the sites with a history of tillage (RC, PF-NP, CRP; Table 2).  Water-stable aggregates were 10 times higher for the TP site compared to the RC site. The CRP and restored prairie sites had values at 72% of the TP site (Table 2).  Saturated hydraulic conductivity values were over 35 times higher for the native prairie (TP) compared to the continuously cropped site (RC), and 2.5 times higher compared to the restored sites (PF-NP, PF- SL, CRP; Table 2). This was attributed to the greater number of macropores (> 1 mm in effective diameter) for the native prairie site.  Soil enzyme activities were consistently highest for TP and PF-SL sites (Table 3), reflecting the close relationship of SOM levels with microbial activity.  Enzyme activity values were generally lowest for soil under continuous cropping (RC) likely due to low SOM and water-stable aggregates (Table 3).  PF-NP soils were lower in dehydrogenase, glucosaminidase, and phosphatase, which may be a reflection of different microbial communities and possible different SOM quality  PF-NP soils were lower in dehydrogenase, glucosaminidase, and phosphatase, which may be a reflection of different microbial communities and possible different SOM quality.  Soil DNA content agreed closely with other indicators of soil quality (SOM, glucosidase) that are associated with microbial activity.  The site with the highest number of bands from molecular analysis of extracted soil DNA, TP with 20, appears to have the greatest bacterial diversity, while soil from RC with 10 bands had the lowest diversity. Soil from the PF and CRP sites had band numbers ranging from 12 to 16, suggesting that this ‘intermediate’ level of diversity is a characteristic response of soil undergoing restoration to its original bacterial community.  The relationship of soil organic matter (SOM) to biological activity is illustrated by strong correlations between soil DNA (representing the bacterial community) and water stable aggregates (r 2 = 0.82) and glucosidase activity (representing SOM decomposition; r 2 = 0.83). Table 1. Characteristics of ecosystems at study sites. Study Site CodeManagement SystemVegetation Tucker PrairieTPUncultivated nativeNative, warm season prairie.grasses and forbs. Prairie Fork – NewPF-NPRow crops until 1993,Little bluestem, Prairienative grasses and side-oats gramma, legumes since 1994.Indian grass. Prairie Fork – SiriceaPF-SLSame as PF-NP.Same as PF-NP with Lespedezainfestation of lespedeza. Centralia-CRPCRPManaged as CRP sinceCool season grasses 1990, no fertility.and forage legumes. Centralia-Row CropRCRotation since 1990, highSoybean (2003), fertility, minimum tillage.corn (2004). Introduction Evaluation of critical soil properties is essential in assessing the restoration of degraded prairies and old cultivated fields to ecosystems that resemble native prairies. Restoration and maintenance of soil quality is highly dependent on organic matter (SOM), an array of soil organisms and biological activity, and improved physical characteristics including water infiltration, macroporosity, aggregate stability, and bulk density.Soils managed under native ecosystems relative to agricultural row crops often have significant differences in soil physical and microbial properties. Assessment of relationships among these properties may provide useful information in how the physical environment affects microbial properties. Evaluation of critical soil properties is essential in assessing the restoration of degraded prairies and old cultivated fields to ecosystems that resemble native prairies. Restoration and maintenance of soil quality is highly dependent on organic matter (SOM), an array of soil organisms and biological activity, and improved physical characteristics including water infiltration, macroporosity, aggregate stability, and bulk density. Soils managed under native ecosystems relative to agricultural row crops often have significant differences in soil physical and microbial properties. Assessment of relationships among these properties may provide useful information in how the physical environment affects microbial properties.Objective The objective of this research was to quantify soil physical properties and soil enzyme activity, physiological and molecular characteristics for native, restored, and cultivated prairies. The objective of this research was to quantify soil physical properties and soil enzyme activity, physiological and molecular characteristics for native, restored, and cultivated prairies. Figure 1. Sites used for the study (a) Tucker Prairie, (b) Prairie Fork- new prairie, (c) Prairie Fork with sericea lespedeza infestation, (d) Centralia CRP, and (e) Centralia row crop rotation (with corn). bcde a Table 2. Soil physical and chemical properties. BulkWater-Stable Hydaulic Study SiteSOMDensity AggregatesConductivity*Porosity %g cm -3 % mm h -1 m 3 m -3 TP d** 40.8a 671a0.619a PF-NP ab 29.4b 243b0.485cd PF-SL c 28.2b 222b0.521b CRP b 30.6b 285b0.497c RC a 3.8c 17.9c0.473d *Geometric means **Means within a column followed by the same letter are not significantly different at P<0.05. Table 3. Microbial enzyme activities and DNA content for the sites. Dehydro-Glucos-Soil Study Site genase aminidaseGlucosidasePhosphataseDNA  g tpf g  g  -nitrophenol g -1 soil  g g -1 soil TP320 a*160 a 350 a 1580 a10.3 PF-NP190 c 90 c 325 ab 640 cd 8.1 PF-SL250 b150 ab 300 bc 1180 b 7.4 CRP260 b130 b 290 c 710 c 8.2 RC120 d 70 c 250 c 400 d 6.2 *Means within a column followed by the same letter are not significantly different at P<0.05. Materials and Methods  Land treatments included native, uncultivated prairie with established warm-season grasses and forbs; 10-yr-old restored prairie dominated by little bluestem (Schizachyrium scoparium),side-oats gramma (Bouteloua curtipendula), and Indian grass (Sorghastrum nutans);10-yr-old restored prairie dominated by sericea lespedeza (Lespedeza cuneata); a 14-yr-old conservation reserve program site with cool-season grasses and low density forage legumes; and a site under row crop production with the past 14 years under a corn (Zea mays)-soybean (Glycine max) rotation cropping system (Fig. 1, Table 1).  Land treatments included native, uncultivated prairie with established warm-season grasses and forbs; 10-yr-old restored prairie dominated by little bluestem (Schizachyrium scoparium), side-oats gramma (Bouteloua curtipendula), and Indian grass (Sorghastrum nutans); 10-yr-old restored prairie dominated by sericea lespedeza (Lespedeza cuneata); a 14-yr-old conservation reserve program site with cool-season grasses and low density forage legumes; and a site under row crop production with the past 14 years under a corn (Zea mays)-soybean (Glycine max) rotation cropping system (Fig. 1, Table 1).  Sampling sites were located on Mexico silt loam (fine, smectitic, mesic Aeric Vertic Epiaqualfs).  Relatively undisturbed cores (7.62 cm by 7.62 cm ) were sampled from the 0 to 10 cm depth on 12 May 2004; 3 replicate locations with 5 sub-samples per location.  Samples were evaluated for physical properties: bulk density, pore-size distributions, saturated hydraulic conductivity and water-stable aggregates. Summary This research demonstrated that soil measurements based on soil enzyme activity, physiological and molecular characteristics, and selected physical traits (water-stable aggregation, saturated hydraulic conductivity) differentiated soils managed as native prairie, restored prairie, or cultivated land. Results indicated that sites under restoration to prairie vegetation are transitional between native prairie and cultivated soils based on combined physical and microbiological analyses. The use of physiological and molecular analyses of prairie soils yielded new insights on the complex functional and structural diversity of their soil bacterial communities, which contribute to the biological characteristics of these soils.