Dynamics of Soil Organic Matter in Tropical Ecosystems
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
Formación De Neologismos En Ciencia Del Suelo
Formación de neologismos en Ciencia del Suelo Formation of Soil Science neologisms Formação de neologismos em Ciência do Solo AUTORES Received: 01.06.2012 Revised: 19.06.2012 Accepted: 20.06.2012 @ 1 Porta J. [email protected]. cat RESUMEN 2 Desde el Congreso de Roma de 1924, en el que la comunidad cientí!ca decidió utilizar la expresión Villanueva D. Soil Science en lugar de Pedology o Edaphology, no se ha llegado a establecer criterios para la formación en español de neologismos referentes! "# al estudio del suelo."$%#& En inglés, los nuevos términos se forman dando prioridad a la raíz griega ! " frente a la raíz # . Este criterio, que se ha consolidado !!"#" con el uso, no tiene en cuenta que en griego el término se"$%#& re!ere al suelo sobre el que se anda y @ Corresponding no al suelo en el que crecen las plantas, expresado por el término # . En el presente trabajo, desde Author una perspectiva etimológica, semántica y de pragmática lingüística, se proponen criterios para la 1 Sociedad Española formación de neologismos en español o al establecer equivalencias en español de voces introducidas de la Ciencia del en inglés. El análisis se basa en voces de autoridad; en elementos etimológicos; en aspectos de am- Suelo. Universitat de Lleida. Rovira Roure bigüedad fonética y ortográ!ca; en la revisión de equivalencias entre términos similares en español, 191, 25198 Lleida, inglés y francés; en el ámbito universitario; en la denominación de las sociedades y revistas cientí!cas; España. y en aspectos de buen gusto idiomático en determinados ámbitos geográ!cos del español. -
Fact Sheet 3: Organic Matter Decline
Sustainable agriculture and soil conservation Soil degradation processes Fact sheet no. 3 Organic matter decline What is organic matter decline? Soil organic matter includes all living soil organisms together with the remains of dead organisms in their various degrees of decomposition. The organic carbon content of a soil is made up of heterogeneous mixtures of both simple and complex substances containing carbon. The sources for organic matter are crop residues, animal and green manures, compost and other organic materials. A decline in organic matter is caused by the reduced presence of decaying organisms, or an increased rate of decay as a result of changes in natural or anthropogenic factors. Organic matter is regarded as a vital component of a healthy soil; its decline results in a soil that is degraded. A soil that is rich in organic matter (Source: Soil Atlas of Europe) Why is soil organic matter/carbon important? Soil organic matter is a source of food for soil fauna, and contributes to soil biodiversity by acting as a reservoir of soil nutrients such as nitrogen, phosphorus and sulphur; it is the main contributor to soil fertility. Soil organic carbon supports the soil’s structure, improving the physical environment for roots to penetrate through the soil. Organic matter absorbs water – it is able to hold about six times its weight in water – making it a lifeline for vegetation in naturally dry and sandy soils. Soils containing organic matter have a better structure that improves water infiltration, and reduces the soil’s susceptibility to compaction, erosion, desertification and landslides. On a global scale, soils contain around twice the amount of carbon held in the atmosphere and three times the amount found in vegetation. -
Effects of Nitrogen Additions on Soil Respiration in an Asian Tropical Montane Rainforest
Article Effects of Nitrogen Additions on Soil Respiration in an Asian Tropical Montane Rainforest Fangtao Wu 1,2, Changhui Peng 1,2,3,* , Weiguo Liu 1,2, Zhihao Liu 1,2, Hui Wang 1,2, Dexiang Chen 4 and Yide Li 4 1 Center for Ecological Forecasting and Global Change, College of Forestry, Northwest A&F University, Yangling 712100, China; [email protected] (F.W.); [email protected] (W.L.); [email protected] (Z.L.); [email protected] (H.W.) 2 State Key Laboratory of Soil Erosion and Dryland Farming on the Loess Plateau, Northwest A&F University, Yangling 712100, China 3 Department of Biology Sciences, Institute of Environment Sciences, University of Quebec at Montreal, C.P. 8888, Succ. Centre-Ville, Montreal, QC H3C 3P8, Canada 4 Jianfengling National Key Field Observation and Research Station for Forest Ecosystem, Research Institute of Tropical Forestry, Chinese Academy of Forestry, Guangzhou 510520, China; [email protected] (D.C.); [email protected] (Y.L.) * Correspondence: [email protected] Abstract: Understanding the impacts of nitrogen (N) addition on soil respiration (RS) and its temper- ature sensitivity (Q10) in tropical forests is very important for the global carbon cycle in a changing environment. Here, we investigated how RS respond to N addition in a tropical montane rainforest in Southern China. Four levels of N treatments (0, 25, 50, and 100 kg N ha−1 a−1 as control (CK), low N (N25), moderate N (N50), and high N (N100), respectively) were established in September 2010. Based on a static chamber-gas chromatography method, R was measured from January 2015 S to December 2018. -
Soils and Fertilizers for Master Gardeners: Soil Organic Matter and Organic Amendments1 Gurpal S
SL273 Soils and Fertilizers for Master Gardeners: Soil Organic Matter and Organic Amendments1 Gurpal S. Toor, Amy L. Shober, and Alexander J. Reisinger2 This article is part of a series entitled Soils and Fertilizers for Master Gardeners. The rest of the series can be found at http://edis.ifas.ufl.edu/topic_series_soils_and_fertil- izers_for_master_gardeners. A glossary can also be found at http://edis.ifas.ufl.edu/MG457. Introduction and Purpose Organic matter normally occupies the smallest portion of the soil physical makeup (approximately 5% of total soil volume on average, and usually 1 to 3% for Florida’s sandy soils) but is the most dynamic soil component (Figure Figure 1. Typical components of soil. 1). The primary sources of soil organic matter are plant Credits: Gurpal Toor and animal residues. Soil organic matter is important for maintaining good soil structure, which enhances the What is the composition of soil movement of air and water in soil. Organic matter also organic matter? plays an important role in nutrient cycling. This publication is designed to educate homeowners about the importance Soil organic matter contains (i) living biomass: plant, of soil organic matter and provide suggestions about how to animal tissues, and microorganisms; (ii) dead tissues: partly build the organic matter in garden and landscape soils. decomposed materials; and (iii) non-living materials: stable portion formed from decomposed materials, also known as humus. Soil organic matter typically contains about 50% carbon. The remainder of soil organic matter consists of about 40% oxygen, 5% hydrogen, 4% nitrogen, and 1% sulfur. The amount of organic matter in soils varies widely, from 1 to 10% (total dry weight) in most soils to more than 90% in organic (muck) soils. -
Tillage and Soil Ecology: Partners for Sustainable Agriculture
Soil & Tillage Research 111 (2010) 33–40 Contents lists available at ScienceDirect Soil & Tillage Research journal homepage: www.elsevier.com/locate/still Review Tillage and soil ecology: Partners for sustainable agriculture Jean Roger-Estrade a,b,*, Christel Anger b, Michel Bertrand b, Guy Richard c a AgroParisTech, UMR 211 INRA/AgroParisTech., Thiverval-Grignon, 78850, France b INRA, UMR 211 INRA/AgroParisTech. Thiverval-Grignon, 78850, France c INRA, UR 0272 Science du sol, Centre de recherche d’Orle´ans, Orle´ans, 45075, France ARTICLE INFO ABSTRACT Keywords: Much of the biodiversity of agroecosystems lies in the soil. The functions performed by soil biota have Tillage major direct and indirect effects on crop growth and quality, soil and residue-borne pests, diseases Soil ecology incidence, the quality of nutrient cycling and water transfer, and, thus, on the sustainability of crop Agroecosystems management systems. Farmers use tillage, consciously or inadvertently, to manage soil biodiversity. Soil biota Given the importance of soil biota, one of the key challenges in tillage research is understanding and No tillage Plowing predicting the effects of tillage on soil ecology, not only for assessments of the impact of tillage on soil organisms and functions, but also for the design of tillage systems to make the best use of soil biodiversity, particularly for crop protection. In this paper, we first address the complexity of soil ecosystems, the descriptions of which vary between studies, in terms of the size of organisms, the structure of food webs and functions. We then examine the impact of tillage on various groups of soil biota, outlining, through examples, the crucial effects of tillage on population dynamics and species diversity. -
The Conditions for Sustainability of Tropical Agriculture. Bioeconomic Models Applied to Five Contrasting Farming Systems
The conditions for sustainability of tropical agriculture. Bioeconomic models applied to five contrasting farming systems. Paper presented for the mini-symposium on modeling at the International Association of Agricultural Economists conference In Berlin August 2000. Bruno Barbier1 and Chantal Carpentier2 Abstract Bioeconomic models (BEMs) are models that simulate biophysical processes and economic activities based on optimization algorithms. This paper describes five applications of BEMs in five contrasted tropical farming systems from Africa and Latin America. The objective of this study is to understand the land use dynamic, assess the strengths and limitations of each agro-ecosystem, and predict the response farmers are likely to give to various external changes such as prices and population growth. Since these models are reasonable approximation of what is likely to happen in the future, we made recommendations about the possibilities of boosting production, alleviating poverty and maintaining the environment. The simulations show contrasting results for each site. The main factor of differentiation between each site is rainfall with the more challenging area being the Sahel. However the more humid area is not the better area. The seemingly better area is the hillside area of Honduras because springs and good access to a large city made intensification a reality. The problems are of different nature in each site. The African villages have the greatest challenges since population growth requires intensification and that intensification under warm climate is more expensive than under colder climate. Indeed the central problem of most African soils is its low natural fertility and then the high oxidation rates which makes permanent cultivation difficult. -
Lactic Acid Bacteria
Sustainable Agriculture August 2013 SA-8 Natural Farming: Lactic Acid Bacteria David M. Ikeda1, Eric Weinert, Jr.1, Kim C.S. Chang1, Joseph M. McGinn1, Sherri A. Miller1 Cheyanne Keliihoomalu2, and Michael W. DuPonte2 1Cho Global Natural Farming Hawai‘i, Hilo, HI 2College of Tropical Agriculture and Human Resources, Cooperative Extension Service, Hilo, HI Introduction for the production of yogurt, cheese, cultured butter, Lactic acid bacteria (LAB) are ubiquitous microorgan- sour cream, sausage, kimchee, olives, and sauerkraut isms that can be beneficial in crop and livestock produc- (Nordqvist 2004). tion. With their long history of use in food preservation by many world cultures (Nordqvist 2004), LAB are How Are LAB Cultured? generally recognized as safe for human consumption. By Step-by-step instructions are given below. Rice grains producing lactic acid as a fermentation metabolite, these are readily available, economical sources of LAB. microorganisms prolong storage, preserve nutritive value, When washing rice with clean water in preparation for and enhance flavors of otherwise perishable foods. LAB cooking, colonies of LAB can be collected in the rinse are easy to collect and economical to culture, store, and water. Microorganisms other than LAB are also pres- use. This fact sheet addresses frequently asked questions ent, but allowing the rice rinse water to sit for 3 to 5 concerning LAB collection, culture, storage, and use in days will cause LAB to become the predominant spe- Natural Farming. cies. Since the rinse water is low in nutrients, milk is then added as a food source for the LAB. Fresh cow’s What Are Lactic Acid Bacteria? or goat’s milk, which is high in lactose (milk sugar), “Lactic acid bacteria” (LAB) refers to a large group is an ideal food source for LAB proliferation, or cul- of bacteria, rather than a single species or strain, that ture. -
Effects of Wheel Traffic and Farmyard Manure Applications on Soil CO2
Turkish Journal of Agriculture and Forestry Turk J Agric For (2018) 42: 288-297 http://journals.tubitak.gov.tr/agriculture/ © TÜBİTAK Research Article doi:10.3906/tar-1709-79 Effects of wheel traffic and farmyard manure applications on soil CO2 emission and soil oxygen content 1, 1 2 Sefa ALTIKAT *, H. Kaan KÜÇÜKERDEM , Aysun ALTIKAT 1 Department of Biosystem Engineering, Faculty of Agriculture, Iğdır University, Iğdır, Turkey 2 Department of Environmental Engineering, Faculty of Engineering, Iğdır University, Iğdır, Turkey Received: 20.09.2017 Accepted/Published Online: 17.04.2018 Final Version: 07.08.2018 Abstract: This 2-year field study investigated the effects of different wheel traffic passes, manure amounts, and manure application methods on soil temperature, soil moisture, CO2 emission, and soil O2 content. To achieve this purpose, three different wheel traffic applications (no traffic, one pass, and two passes) were used. In the experiments, two different methods of manure applications (surface and subsurface) and three different farmyard manure amounts were used with a control plot (N0), 40 Mg ha–1 (N40), and 80 Mg ha–1 (N80). Manure was applied in both years of the experiment in the first week of April. For the subsurface application, the manure was mixed in at approximately 10 cm of soil depth with a rotary tiller. According to the results, soil temperature, soil moisture, penetration resistance, and bulk density increased with increasing wheel traffic except 2CO emission for 2014 and 2015. CO2 emission values decreased with traffic. Subsurface manure application caused more 2CO emission compared to surface application. The increase in manure amounts led to an increase in CO2 emission and soil moisture content. -
National University of Engineering Ge111
NATIONAL UNIVERSITY OF ENGINEERING COLLEGE OF ENVIRONMENTAL ENGINEERING ENVIRONMENTAL ENGINEERING PROGRAM GE111 – EDAPHOLOGY I. GENERAL INFORMATION CODE : GE111 – Edaphology SEMESTER : 5 CREDITS : 03 HOURS PER WEEK : 04 (Theory – Practices – Laboratory) PREREQUISITES : GE102 – Geography CONDITION : Mandatory II. COURSE DESCRIPTION Concept and importance of edaphological soil and its interest for Engineering. Detailed knowledge of the components, physical and chemical properties, genesis, classification and principles of cartography, of natural soils and anthropogenic urban soils. Principle of soil evaluation, as a starting point in studies of environmental planning, territorial planning and environmental impact assessment. Finally, it is intended that students understand the importance of soil as a non-renewable resource and the degradations to which its inappropriate use leads; It is also intended to train in the corrective and rehabilitating measures of degraded soils. III. COURSE OUTCOMES At the end of the course the student will: Organizes data for proper analysis and interpretation and calculations (soil densities, physical chemical and biological properties). Explains and determines the genesis of the soil, the physical properties of the soil, geo reference, physiographic units. Understand and apply densities, to determine the consistency of the soil, the probability of resistance in an earthquake. Interpret and perform types of soil sampling to take to the laboratory to determine their physical, chemical, and biological characteristics. Build models to determine the degree of contamination, is determined by the parameters, using the LMOs, ECAs, In soils. IV. LEARNING UNITS 1. SOIL GENESIS / 4 HOURS Objective of soil science: Interest in Engineering. Genesis. Pedological and edaphological approach. Factors of soil formation. Climate action. Properties of the soil affected by the climate. -
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. -
Soil Quality: Why and How?
Geoderma 114 (2003) 145–156 www.elsevier.com/locate/geoderma Soil quality: why and how? Douglas L. Karlena,*, Craig A. Ditzlerb, Susan S. Andrewsa a USDA-ARS National Soil Tilth Laboratory, 2150 Pammel Drive, Ames, IA 50011-4420, USA b National Soil Survey Center, 100 Centennial Mall North, Lincoln, NE 68508-3866, USA Abstract The soil quality concept evolved throughout the 1990s in response to increased global emphasis on sustainable land use and with a holistic focus emphasizing that sustainable soil management requires more than soil erosion control. The concept includes two areas of emphasis—education and assessment—both based soundly on principles of soil science. Soil quality test kits, farmer-based scorecards, visual assessment procedures, fact sheets, and video presentations were developed as educational materials because many people have no basis to recognize, understand or appreciate the complexity of soil resources. Assessment tools for indexing soil quality at various scales were pursued to show the multiple functions (e.g. nutrient and water cycling, filtering and buffering of contaminants, decomposition of crop residues and other organic matter sources, and recycling of essential plant nutrients) that soils provide as the foundation for sustainable land management. Worldwide research and technology transfer efforts have increased awareness that soil resources have both inherent characteristics determined by their basic soil formation factors and dynamic characteristics influenced by human decisions and management practices. Soil quality assessment and education are intended to provide a better understanding and awareness that soil resources are truly living bodies with biological, chemical, and physical properties and processes performing essential ecosystem services. -
Late Holocene Climate Reconstructions for the Russian Steppe, Based on Mineralogical and Magnetic Properties of Buried Palaeosols ⁎ T
Palaeogeography, Palaeoclimatology, Palaeoecology 249 (2007) 103–127 www.elsevier.com/locate/palaeo Late Holocene climate reconstructions for the Russian steppe, based on mineralogical and magnetic properties of buried palaeosols ⁎ T. Alekseeva a, A. Alekseev a, , B.A. Maher b, V. Demkin a a Institute of Physicochemical and Biological Problems of Soil Science, Russian Academy of Sciences, Pushchino, Russia b Centre for Environmental Magnetism and Palaeomagnetism, Lancaster Environment Centre, Department of Geography, Lancaster University, Lancaster, LA1 4YB, UK Received 10 April 2005; received in revised form 29 December 2006; accepted 15 January 2007 Abstract Insights into past climate changes, and corresponding evolution of soils and the environment, can be gained by multi- disciplinary studies of palaeosols. Here, we focus on palaeosols buried beneath archaeological monuments, specifically, funerary mounds (kurgans), in the Russian steppe. The kurgans were constructed, and each of the palaeosols buried, over a range of different timesteps from the mid-Holocene to ∼ 600 years before present (yr BP). Integrated magnetic, mineralogical and pedological data were used to obtain estimates of past climate (especially precipitation) changes, through both time and space. A soil magnetism- based climofunction, derived previously from modern steppe soils and modern climate, was applied to each set of palaeosols, to obtain quantitative reconstructions of annual precipitation for the time at which the soils were buried. Independent soil property data (clay mineralogy, salt content, iron mineralogy from Mossbauer analysis, and optical and electron microscopy) were also obtained, in order to test and substantiate the magnetic inferences. The data obtained indicate that the climate of the Lower Volga steppe area has varied from the mid-Holocene onwards.