Biological Soil Crusts
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Long-Term Changes in Biological Soil Crust Cover and Composition Eva Dettweiler-Robinson1*, Jeanne M Ponzetti2 and Jonathan D Bakker3
Dettweiler-Robinson et al. Ecological Processes 2013, 2:5 http://www.ecologicalprocesses.com/content/2/1/5 RESEARCH Open Access Long-term changes in biological soil crust cover and composition Eva Dettweiler-Robinson1*, Jeanne M Ponzetti2 and Jonathan D Bakker3 Abstract Introduction: Communities change over time due to disturbances, variations in climate, and species invasions. Biological soil crust communities are important because they contribute to erosion control and nutrient cycling. Crust types may respond differently to changes in environmental conditions: single-celled organisms and bryophytes quickly recover after a disturbance, while lichens are slow growing and dominate favorable sites. Community change in crusts has seldom been assessed using repeated measures. For this study, we hypothesized that changes in crust composition were related to disturbance, topographic position, and invasive vegetation. Methods: We monitored permanent plots in the Columbia Basin in 1999 and 2010 and compared changes in crust composition, cover, richness, and turnover with predictor variables of herbivore exclosure, elevation, heat load index, time since fire, presence of an invasive grass, and change in cover of the invasive grass. Results: Bryophytes were cosmopolitan with high cover. Dominant lichens did not change dramatically. Indicator taxa differed by monitoring year. Bryophyte and total crust cover declined, and there was lower turnover outside of herbivore exclosures. Lichen cover did not change significantly. Plots that burned recently had high turnover. Increase in taxon richness was correlated with presence of an invasive grass in 1999. Change in cover of the invasive grass was positively related to proportional loss and negatively related to gain. Conclusions: Composition and turnover metrics differed significantly over 11 years, though cover was more stable between years. -
Agricultural Soil Compaction: Causes and Management
October 2010 Agdex 510-1 Agricultural Soil Compaction: Causes and Management oil compaction can be a serious and unnecessary soil aggregates, which has a negative affect on soil S form of soil degradation that can result in increased aggregate structure. soil erosion and decreased crop production. Soil compaction can have a number of negative effects on Compaction of soil is the compression of soil particles into soil quality and crop production including the following: a smaller volume, which reduces the size of pore space available for air and water. Most soils are composed of • causes soil pore spaces to become smaller about 50 per cent solids (sand, silt, clay and organic • reduces water infiltration rate into soil matter) and about 50 per cent pore spaces. • decreases the rate that water will penetrate into the soil root zone and subsoil • increases the potential for surface Compaction concerns water ponding, water runoff, surface soil waterlogging and soil erosion Soil compaction can impair water Soil compaction infiltration into soil, crop emergence, • reduces the ability of a soil to hold root penetration and crop nutrient and can be a serious water and air, which are necessary for water uptake, all of which result in form of soil plant root growth and function depressed crop yield. • reduces crop emergence as a result of soil crusting Human-induced compaction of degradation. • impedes root growth and limits the agricultural soil can be the result of using volume of soil explored by roots tillage equipment during soil cultivation or result from the heavy weight of field equipment. • limits soil exploration by roots and Compacted soils can also be the result of natural soil- decreases the ability of crops to take up nutrients and forming processes. -
Biological Soil Crust Community Types Differ in Key Ecological Functions
UC Riverside UC Riverside Previously Published Works Title Biological soil crust community types differ in key ecological functions Permalink https://escholarship.org/uc/item/2cs0f55w Authors Pietrasiak, Nicole David Lam Jeffrey R. Johansen et al. Publication Date 2013-10-01 DOI 10.1016/j.soilbio.2013.05.011 Peer reviewed eScholarship.org Powered by the California Digital Library University of California Soil Biology & Biochemistry 65 (2013) 168e171 Contents lists available at SciVerse ScienceDirect Soil Biology & Biochemistry journal homepage: www.elsevier.com/locate/soilbio Short communication Biological soil crust community types differ in key ecological functions Nicole Pietrasiak a,*, John U. Regus b, Jeffrey R. Johansen c,e, David Lam a, Joel L. Sachs b, Louis S. Santiago d a University of California, Riverside, Soil and Water Sciences Program, Department of Environmental Sciences, 2258 Geology Building, Riverside, CA 92521, USA b University of California, Riverside, Department of Biology, University of California, Riverside, CA 92521, USA c Biology Department, John Carroll University, 1 John Carroll Blvd., University Heights, OH 44118, USA d University of California, Riverside, Botany & Plant Sciences Department, 3113 Bachelor Hall, Riverside, CA 92521, USA e Department of Botany, Faculty of Science, University of South Bohemia, Branisovska 31, 370 05 Ceske Budejovice, Czech Republic article info abstract Article history: Soil stability, nitrogen and carbon fixation were assessed for eight biological soil crust community types Received 22 February 2013 within a Mojave Desert wilderness site. Cyanolichen crust outperformed all other crusts in multi- Received in revised form functionality whereas incipient crust had the poorest performance. A finely divided classification of 17 May 2013 biological soil crust communities improves estimation of ecosystem function and strengthens the Accepted 18 May 2013 accuracy of landscape-scale assessments. -
Anatomy of a Sub-Cambrian Paleosol in Wisconsin
Anatomy of a Sub-Cambrian Paleosol in Wisconsin: Mass Fluxes of Chemical Weathering and Climatic Conditions in North America during Formation of the Cambrian Great Unconformity L. Gordon Medaris Jr.,1,* Steven G. Driese,2 Gary E. Stinchcomb,3 John H. Fournelle,1 Seungyeol Lee,1,4 Huifang Xu,1,4 Lyndsay DiPietro,2 Phillip Gopon,5 and Esther K. Stewart6 1. Department of Geoscience, University of Wisconsin, Madison, Wisconsin 53706, USA; 2. Department of Geosciences, Terrestrial Paleoclimatology Research Group, Baylor University, Waco, Texas 76798, USA; 3. Department of Geosciences and Watershed Studies Institute, Murray State University, Murray, Kentucky 42071, USA; 4. NASA Astrobiology Institute, University of Wisconsin, Madison, Wisconsin 53706, USA; 5. Department of Earth Sciences, University of Oxford, South Parks Road, Oxford OX1 3AN, United Kingdom; 6. Wisconsin Geological and Natural History Survey, Madison, Wisconsin 53705, USA ABSTRACT A paleosol beneath the Upper Cambrian Mount Simon Sandstone in Wisconsin provides an opportunity to evaluate the characteristics of Cambrian weathering in a subtropical climate, having been located at 207S paleolatitude 500 My ago. The 285-cm-thick paleosol resulted from advanced chemical weathering of a gabbroic protolith, recording a total mass loss of 50%. Weathering of hornblende and plagioclase produced a pedogenic assemblage of quartz, chlorite, kaolinite, goethite, and, in the lowest part of the profile, siderite. Despite the paucity of quartz in the protolith and 40% removal of SiO2 from the profile, quartz constitutes 11%–23% of the pedogenic mineral assemblage. Like many other Precambrian and Cambrian paleosols in the Lake Superior region, the paleosol experienced potassium metasomatism, now con- taining 10%–25% mixed-layer illite-vermiculite and 5%–44% potassium feldspar. -
Soil Crusts Structural Soil Crusts Are Relatively Thin, Dense, Somewhat Continuous Layers of Non-Aggregated Soil Particles on the Surface of Tilled and Exposed Soils
Indicator Test Function USDA Natural Resources Conservation Service P F W Soil Quality Indicators Soil Crusts Structural soil crusts are relatively thin, dense, somewhat continuous layers of non-aggregated soil particles on the surface of tilled and exposed soils. Structural crusts develop when a sealed-over soil surface dries out after rainfall or irrigation. Water droplets striking soil aggregates and water flowing across soil breaks aggregates into individual soil particles. Fine soil particles wash, settle into and block surface pores causing the soil surface to seal over and preventing water from soaking into the soil. As the muddy soil surface dries out, it crusts over. Left: Note the surface crust on this soil. The field was in tall fescue sod for 11 years. It was cleared and plowed using conventional Structural crusts range from a few tenths to as thick as two tillage methods. Photo courtesy Bobby Brock, USDA NRCS (retired). Right: Collected from a no-till field in Georgia’s Southern inches. A surface crust is much more compact, hard and Piedmont, good structure and aggregation are evident in the soil on brittle when dry than the soil immediately beneath it, the right. The same soil formed a structural crust under which may be loose and friable. Crusts can be described by conventional tillage. Note the sunlight reflectance of the crusted their strength, or air-dry rupture resistance. soil. Photo courtesy James E. Dean, USDA NRCS (retired). Soil crusting is also associated with biological and Dynamic - Management activities that deplete soil chemical factors. A biological crust is a living community organic matter and leave soil bare, smooth and exposed to of lichen, cyanobacteria, algae, and moss growing on the the direct impact of water droplets increase soil dispersion, soil surface that bind the soil together. -
Biological Soil Crust Rehabilitation in Theory and Practice: an Underexploited Opportunity Matthew A
REVIEW Biological Soil Crust Rehabilitation in Theory and Practice: An Underexploited Opportunity Matthew A. Bowker1,2 Abstract techniques; and (3) monitoring. Statistical predictive Biological soil crusts (BSCs) are ubiquitous lichen–bryo- modeling is a useful method for estimating the potential phyte microbial communities, which are critical structural BSC condition of a rehabilitation site. Various rehabilita- and functional components of many ecosystems. How- tion techniques attempt to correct, in decreasing order of ever, BSCs are rarely addressed in the restoration litera- difficulty, active soil erosion (e.g., stabilization techni- ture. The purposes of this review were to examine the ques), resource deficiencies (e.g., moisture and nutrient ecological roles BSCs play in succession models, the augmentation), or BSC propagule scarcity (e.g., inoc- backbone of restoration theory, and to discuss the prac- ulation). Success will probably be contingent on prior tical aspects of rehabilitating BSCs to disturbed eco- evaluation of site conditions and accurate identification systems. Most evidence indicates that BSCs facilitate of constraints to BSC reestablishment. Rehabilitation of succession to later seres, suggesting that assisted recovery BSCs is attainable and may be required in the recovery of of BSCs could speed up succession. Because BSCs are some ecosystems. The strong influence that BSCs exert ecosystem engineers in high abiotic stress systems, loss of on ecosystems is an underexploited opportunity for re- BSCs may be synonymous with crossing degradation storationists to return disturbed ecosystems to a desirable thresholds. However, assisted recovery of BSCs may trajectory. allow a transition from a degraded steady state to a more desired alternative steady state. In practice, BSC rehabili- Key words: aridlands, cryptobiotic soil crusts, cryptogams, tation has three major components: (1) establishment of degradation thresholds, state-and-transition models, goals; (2) selection and implementation of rehabilitation succession. -
The Use of Proximal Soil Sensor Data Fusion and Digital Soil Mapping For
The use of proximal soil sensor data fusion and digital soil mapping for precision agriculture Wenjun Ji, Viacheslav Adamchuk, Songchao Chen, Asim Biswas, Maxime Leclerc, Raphael Viscarra Rossel To cite this version: Wenjun Ji, Viacheslav Adamchuk, Songchao Chen, Asim Biswas, Maxime Leclerc, et al.. The use of proximal soil sensor data fusion and digital soil mapping for precision agriculture. Pedometrics 2017, Jun 2017, Wageningen, Netherlands. 298 p. hal-01601278 HAL Id: hal-01601278 https://hal.archives-ouvertes.fr/hal-01601278 Submitted on 2 Jun 2020 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Distributed under a Creative Commons Attribution - ShareAlike| 4.0 International License Abstract Book Pedometrics 2017 Wageningen, 26 June – 1 July 2017 2 Contents Evaluating Use of Ground Penetrating Radar and Geostatistic Methods for Mapping Soil Cemented Horizon .................................... 13 Digital soil mapping in areas of mussunungas: algoritmos comparission .......... 14 Sensing of farm and district-scale soil moisture content using a mobile cosmic ray probe (COSMOS Rover) .................................... 15 Proximal sensing of soil crack networks using three-dimensional electrical resistivity to- mography ......................................... 16 Using digital microscopy for rapid determination of soil texture and prediction of soil organic matter ..................................... -
Water Regulation in Cyanobacterial Biocrusts from Drylands: Negative Impacts of Anthropogenic Disturbance
water Article Water Regulation in Cyanobacterial Biocrusts from Drylands: Negative Impacts of Anthropogenic Disturbance Yolanda Cantón 1,2,*, Sonia Chamizo 1,2, Emilio Rodriguez-Caballero 1,2 , Roberto Lázaro 3, Beatriz Roncero-Ramos 1 , José Raúl Román 1 and Albert Solé-Benet 3 1 Department of Agronomy, University of Almeria, Carretera de Sacramento sn., La Cañada de San Urbano, 04120 Almeria, Spain; [email protected] (S.C.); [email protected] (E.R.-C.); [email protected] (B.R.-R.); [email protected] (J.R.R.) 2 Research Centre for Scientific Collections from the University of Almería (CECOUAL), Carretera de Sacramento sn., La Cañada de San Urbano, 04120 Almeria, Spain 3 Experimental Station of Arid Zones, CSIC, Carretera de Sacramento sn., La Cañada de San Urbano, 04120 Almeria, Spain; [email protected] (R.L.); [email protected] (A.S.-B.) * Correspondence: [email protected] Received: 26 December 2019; Accepted: 4 March 2020; Published: 6 March 2020 Abstract: Arid and semi-arid ecosystems are characterized by patchy vegetation and variable resource availability. The interplant spaces of these ecosystems are very often covered by cyanobacteria-dominated biocrusts, which are the primary colonizers of terrestrial ecosystems and key in facilitating the succession of other biocrust organisms and plants. Cyanobacterial biocrusts regulate the horizontal and vertical fluxes of water, carbon and nutrients into and from the soil and play crucial hydrological, geomorphological and ecological roles in these ecosystems. In this paper, we analyze the influence of cyanobacterial biocrusts on water balance components (infiltration-runoff, evaporation, soil moisture and non-rainfall water inputs (NRWIs)) in representative semiarid ecosystems in southeastern Spain. -
National Cooperative Soil Survey and Biological Soil Crusts
Biological Soil Crusts Status Report 2003 National Cooperative Soil Survey Conference Plymouth, Massachusetts June 16 - 20, 2003 Table of Contents I. NCSS 2003 National Conference Proceedings II. Report and recommendations of the soil crust task force - 2002 West Regional Cooperative Soil Survey Conference Task Force Members Charges Part I. Executive Summary and Recommendations Part II. Report on Charges Part III. Research Needs, Action Items, Additional Charges Part IV. Resources for Additional Information Part V. Appendices Appendix 1 - Agency needs Appendix 2 - Draft material for incorporation into the Soil Survey Manual Introduction Relationship to Mineral Crusts Types of Biological Soil Crusts Figure 1. Biological soil crust types. Major Components of Soil Crusts: Cyanobacteria, Lichens, and Mosses Table 1. Morphological groups for biological crust components and their N-fixing characteristics. (Belnap et al. 2001) Soil Surface Roughness/Crust Age Distribution of Crusts References Appendix 3 - Guidelines for describing soil surface features, Version 2.0 Surface features Table 1. Surface features Determining Percent Cover Equipment Method 1. Step-point Method 2. Ocular estimate with quadrats Method 3. Line-point quadrat Method 4. Stratified line-point intercept Method 5. Ocular estimate Appendix 3a - Data sheets used in Moab field test Appendix 4 - Soil descriptions Discussion Group 1 Group 3 Group 2 Group 4 Appendix 5 - Photography Biological Soil Crust Status Report NCSS National Conference June 16-20, 2003 Table of Contents III. Task force's response to the following questions posed by the 2002 West Regional Standards Committee 1. Are biological soil crusts plants, soil or combination of both? 2. Is it appropriate to think of these crusts as plant communities with potentials, state and transition? 3. -
A Field Guide to Biological Soil Crusts of Western U.S. Drylands Common Lichens and Bryophytes
A Field Guide to Biological Soil Crusts of Western U.S. Drylands Common Lichens and Bryophytes Roger Rosentreter Matthew Bowker Jayne Belnap Photographs by Stephen Sharnoff Roger Rosentreter, Ph.D. Bureau of Land Management Idaho State Office 1387 S. Vinnell Way Boise, ID 83709 Matthew Bowker, Ph.D. Center for Environmental Science and Education Northern Arizona University Box 5694 Flagstaff, AZ 86011 Jayne Belnap, Ph.D. U.S. Geological Survey Southwest Biological Science Center Canyonlands Research Station 2290 S. West Resource Blvd. Moab, UT 84532 Design and layout by Tina M. Kister, U.S. Geological Survey, Canyonlands Research Station, 2290 S. West Resource Blvd., Moab, UT 84532 All photos, unless otherwise indicated, copyright © 2007 Stephen Sharnoff, Ste- phen Sharnoff Photography, 2709 10th St., Unit E, Berkeley, CA 94710-2608, www.sharnoffphotos.com/. Rosentreter, R., M. Bowker, and J. Belnap. 2007. A Field Guide to Biological Soil Crusts of Western U.S. Drylands. U.S. Government Printing Office, Denver, Colorado. Cover photos: Biological soil crust in Canyonlands National Park, Utah, cour- tesy of the U.S. Geological Survey. 2 Table of Contents Acknowledgements ....................................................................................... 4 How to use this guide .................................................................................... 4 Introduction ................................................................................................... 4 Crust composition .................................................................................. -
Forest and Rangeland Soils of the United
Richard V. Pouyat Deborah S. Page-Dumroese Toral Patel-Weynand Linda H. Geiser Editors Forest and Rangeland Soils of the United States Under Changing Conditions A Comprehensive Science Synthesis Forest and Rangeland Soils of the United States Under Changing Conditions Richard V. Pouyat • Deborah S. Page-Dumroese Toral Patel-Weynand • Linda H. Geiser Editors Forest and Rangeland Soils of the United States Under Changing Conditions A Comprehensive Science Synthesis Editors Richard V. Pouyat Deborah S. Page-Dumroese Northern Research Station Rocky Mountain Research Station USDA Forest Service USDA Forest Service Newark, DE, USA Moscow, ID, USA Toral Patel-Weynand Linda H. Geiser Washington Office Washington Office USDA Forest Service USDA Forest Service Washington, DC, USA Washington, DC, USA ISBN 978-3-030-45215-5 ISBN 978-3-030-45216-2 (eBook) https://doi.org/10.1007/978-3-030-45216-2 © The Editor(s) (if applicable) and The Author(s) 2020 . This book is an open access publication. Open Access This book is licensed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license and indicate if changes were made. The images or other third party material in this book are included in the book’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the book’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. -
Microbial Biobanking – Cyanobacteria-Rich Topsoil Facilitates Mine Rehabilitation
Biogeosciences, 16, 2189–2204, 2019 https://doi.org/10.5194/bg-16-2189-2019 © Author(s) 2019. This work is distributed under the Creative Commons Attribution 4.0 License. Microbial biobanking – cyanobacteria-rich topsoil facilitates mine rehabilitation Wendy Williams1, Angela Chilton2, Mel Schneemilch1, Stephen Williams1, Brett Neilan3, and Colin Driscoll4 1School of Agriculture and Food Sciences, The University of Queensland, Gatton Campus 4343, Australia 2Australian Centre for Astrobiology and School of Biotechnology and Biomolecular Sciences, University of New South Wales, Sydney, NSW, 2052, Australia 3School of Environmental and Life Sciences, University of Newcastle, Callaghan, NSW, 2308, Australia 4Hunter Eco, P.O. Box 1047, Toronto, NSW, 2283, Australia Correspondence: Wendy Williams ([email protected]) Received: 13 November 2017 – Discussion started: 20 November 2017 Revised: 10 January 2019 – Accepted: 23 January 2019 – Published: 28 May 2019 Abstract. Restoration of soils post-mining requires key so- tial for biocrust re-establishment. In general, the resilience lutions to complex issues through which the disturbance of of cyanobacteria to burial in topsoil stockpiles in both the topsoil incorporating soil microbial communities can result short and long term was significant; however, in an arid en- in a modification to ecosystem function. This research was in vironment recolonisation and community diversity could be collaboration with Iluka Resources at the Jacinth–Ambrosia impeded by drought. Biocrust re-establishment during mine (J–A) mineral sand mine located in a semi-arid chenopod rehabilitation relies on the role of cyanobacteria as a means shrubland in southern Australia. At J–A, assemblages of mi- of early soil stabilisation. At J–A mine operations do not croorganisms and microflora inhabit at least half of the soil threaten the survival of any of the organisms we studied.