Division 2 - Soil Properties and Processes - Paper Submission

Listed below are the Symposia for each of the Divisions, Commissions and Working Groups available within Division 2.

 

 

 

 

 

 

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DIVISIONAL SYMPOSIA

2.1 Wetland soils and global change

Biogeochemical processes in wetland soils and their role in global change.

Large areas of the world are covered by natural wetlands or soils which are regularly flooded by irrigation. These soils play an important role in food production, biodiversity and ecology, water resources, carbon sequestration, and climate change. This symposium will discuss the current state of knowledge on the biogeochemical cycling of elements in wetland soils. Topics may include the formation and emission of climate-relevant trace gases, carbon sequestration, nitrogen fixation, denitrification, chemical weathering and formation of secondary minerals under anoxic conditions, and the biogeochemistry of trace elements in wetland soils (e.g., Hg, As).

2.2 Managing landscapes for the future

How do we manage our landscapes to provide economic, social and environmental services for the future?

The long term ability of our landscape of producing more food with less water, in a socially and environmentally sustainable manner are challenges that must be addressed through research that integrates across disciplines and scales. Furthermore climate change and energy (depletion of fossil fuels) now command greater attention. Many of the contemporary environmental problems are being approached by stakeholders on the geographic basis of catchments or river basins, where the underlying physical, biological, and chemical science is complex. This session will focus on defining the fundamental disciplinary knowledge needed to explore the interactions among hydrology, biology, geochemistry, and water productivity to better manage our landscapes in a sustainable manner.

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COMMISSION 2.1 - SOIL PHYSICS

2.1.1 Optimizing water use with soil physics

Optimizing the use of limited water: how soil physics research and models can help

There is a global thirst for knowledge on how to overcome the threats by posed by depleting freshwater reserves. Soil physics can play a major role in finding ways to conserve and make the most efficient use of water for crop production to support our growing population, maintain its quality, preserve natural ecosystems and address projected effects of climate change on water. This session will focus on recent advances in understanding and modelling: 1) the infiltration and retention of water in soil and the management practices that enhance these; 2) the old questions of when to apply irrigation water and how much to apply for optimal crop performance; 3) associated optimal applications of N and other nutrients; and 3) more efficient cropping and management scenarios for current and future climate change conditions. Specific interest will be placed on novel solutions to harness and preserve water in soil, the potential impacts of drought resistant crop varieties and new plants with better water use efficiency, and predictions of the threats posed by water scarcity in the future. Recent advances in modelling of evapo-transpiration and solutes from the pore to larger scales, and their implications to water scarcity, are also major topics of this session.

2.1.2 The physics of soil pore structure dynamics

The physics of soil pore structure dynamics

One of the greatest challenges in describing soil physical processes is the continuously changing pore structure that regulates flow and transport. Shrinking and swelling through cycles of wetting and drying, instabilities like slumping and slaking and external stresses from vehicles and overburden can all alter pore structure considerably over time. Coupled hydrological and mechanical models have been developed to account for the deformation of the pore matrix. This work is complemented by fundamental studies on the underlying physical processes that drive changes in pore structure at multiple scales. Some of this work even tackles the thermodynamics of pore structure evolution. This session focuses on the physical processes that drive pore structure dynamics and the impacts on flow and transport properties. 


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COMMISSION 2.2 SOIL CHEMISTRY

2.2.1 Biogeochemical interfaces in soils

Biogeochemical interfaces in soils – molecular process govern functions

Soil is intimately involved in the absorption, storage, transfer and release of heat, water, gases and chemical constituents and has a distinct influence on the environments of all living organisms. Changes in land use, soil management and environmental parameters have distinct impact on these processes. The main locations where these processes and interactions occur are the interfaces between solid, liquid and gaseous phases in soil. The major challenge is to link processes on the atomistic and molecular level to mechanisms observed in the micro and plot scale. In the field of soil chemistry, we have observed a rapid development of emerging characterization and probing techniques adopted from the fields of analytical and computational chemistry, as well as more physically oriented methods from material and nano-sciences. Novel spectroscopic, microsocopic and tomographic techniques in combination with advanced approaches in computational chemistry allow the exploration of the architecture of biogeochemical interfaces and reveal direct information on their structure and dynamics. This session will focus especially on the recent developments of these techniques and on their application on contaminant - soil interactions including biological surfaces. The major focus of the symposium will be on the atomistic, molecular up to the microscale level.

2.2.2 Dynamics of organic materials in soils

Dynamics and fate of natural and waste organic material in soils

Tremendous amounts of by-product organic materials are produced each year from agriculture, domestic and municipal systems, agro-food industries and enterprises, pulp and paper mills, and others. Some of these organic materials are deliberately produced to manage and amend soil properties (eg. crop stubble residues left in-situ), while those from other sources have the potential to be used to amend soils. Together with the combustion of fossil fuels, they can strongly contribute to the carbon emissions into the atmosphere if not properly managed, therefore affecting the fundamental biogeochemical cycling of elements, favouring the exploitation of natural resources and contributing to the overall climatic changes.

Application of organic wastes to natural and agricultural soils may significantly contribute to the reduction of gas emissions, favor the restoration and reclamation of marginal lands, improve the amount and quality of stable organic matter and fight against progressive desertification processes. This session will discuss the latest result of long- and short-term experiments of treated and untreated organic waste application to soils. It will describe the chemical and biochemical transformation of residual materials, and provide novel insights on the potential mobility and (bio)availability of inorganic and organic contaminants (pathogens, hormones, metals, etc.) applied with wastes widely occurring in soil amendments.

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COMMISSION 2.3 - SOIL BIOLOGY

2.3.1 The soil-root interface

The soil-root interface: microbial community dynamics and microbe-plant communications (Joint with 2.5)

Soil in the vicinity of the root (the rhizosphere) presents a higher microbial biomass and microbial activity than the bulk soil due to rhizo-deposition: the release of low and high molecular weight compounds by the root. The large variety of chemicals in the rhizosphere influences many processes that control plant growth, microbial infections and nutrient uptake. Beneficial (e.g. bio-control, mycorrhizal and rhizobial symbioses, nutrient transformation and uptake) and harmful (e.g. phytopathogens, inorganic and organic phytoxicity, nutrient immobilization, climate change induced stress) interactions and their manipulation are of great topical interest. Model systems are available to study processes and changes in microbial communities in the rhizosphere soil. In recent years we have seen a rapid development of innovative techniques to: quantify rhizodeposition, assess microbial diversity and gene expression (mRNA characterization and proteomics), monitor the flow of root exudates to microbial communities, and characterise the many and often-specific signals involved in root-root and root-microbe communications. This symposium will focus on the recent development of these techniques and their application to the study microbial diversity and gene expression in the rhizosphere and a better understanding of microbe-plant interactions.

2.3.2 Gene expression and proteomics in soil

Gene expression and proteomics in soil

Molecular techniques have mainly applied in soil to characterise DNA so as to assess microbial diversity whereas few studies have been carried out to monitor gene expression by extraction and characterization of mRNA and proteins. Novel techniques are available to extract mRNA from soil with successive characterisation. Functional metagenomics based on cloning of large genomic inserts containing operons and promoters can allow screening for specific functions and novel bioproducts. Soil proteomics can give useful information on cell-environment processes, by analysing proteins acting as biosensors, extracellualr enzyme activities, stress proteins and metabolic proteins, and on homologous and heterologous cell-to cell interactions with analysis of proteins or peptides involved in quorum sensing and genetic exchange activities, or defining competition, predation, commensalims and symbiosis. We will encourage presentations which emphasise metagenomic and proteomic studies aimed to better characterise soil functionality.

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COMMISSION 2.4 - SOIL MINERALOGY

2.4.1 Soil minerals and sustainability

The role of soil minerals in forming and maintaining associations in soils to ensure their future sustainability

Soils are primarily composed of associations of minerals with organic compounds, microbes and solutes. The formation of these associations constitutes a basic feature of the genesis of soils and governs their capacity to sequester and store carbon and plant nutrients. These associations also provide habitats for microbes to perform their vital role as decomposers of plant and animal debris and even minerals. This session will focus on the inorganic component in soil associations. It will include examination of the mechanisms whereby different minerals contribute to the formation and stabilisation of complexes involving biochemical compounds including carbohydrates, proteins, and humic substances. It should also discuss the consequences of these mechanisms for devising management systems to enhance the sustainability of soils and of their environmental and agronomic functions.

Encouragement will be given to the definition of those properties of minerals, e.g. measures of surface area, charge and micro-porosity, which influence their abilities to associate with other entities, and the use of these properties to explain and predict the useful functions of soils. The interaction of minerals with microbes deserves attention in this session because it affects the minerals through their alteration, as well as influencing their associations with the other entities in soils. Contributions on advances in instrumental techniques such as electron microscopy and atomic force microscopy which can be used to examine the microenvironment interactions will be welcome.

2.4.2 Soil minerals and contaminants

Soil minerals for the uptake and control of contaminants (Joint with 2.2)

Soils often come into contact with contaminants, which may be heavy metals, metalloids, excess nutrients, e.g. N, P and dissolved organic C, biochemical wastes, or xenobiotic organic compounds. Soils are sometimes used as filters of contaminants, or for their containment. As the most reactive inorganic materials in soils, minerals, and particularly those of clay-size are able to adsorb, immobilise and even transform the various contaminants to varying extents. While there have been many studies of the adsorption of each of the various contaminants by clay minerals, these latter have most often been well-crystallised examples obtained from pure geological deposits or by laboratory synthesis. Few studies have considered interaction of contaminants in multi-component solutions with the imperfectly and poorly crystallised minerals commonly found in soils. These latter include poorly ordered nano-particulate materials (PONM). In this session, contributions will be welcomed on:

1.    The particular characteristics of minerals, e.g. their surface chemistry and microstructure, that affect the adsorption of each contaminant type
2.    Methods for the modification of soil minerals to enhance contaminant uptake, and
3.    The effect of competing species, including organic compounds. Encouragement will be given to studies employing modern instrumental techniques, such as synchrotron-based X-ray absorption spectroscopy, as well as electron and atomic force microscopy, electron spectroscopy and NMR.

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COMMISSION 2.5 - SOIL CHEMICAL, PHYSICAL AND BIOLOGICAL INTERFACIAL INTERACTIONS

2.5.1 Extracellular proteins and nucleic acids in soil

Extracellular proteins and nucleic acids in soil and consequences for microbes, plants and environmental quality (Joint with 2.3)

Surface-reactive inorganic and organic soil particles concentrate biologically-important molecules in their near vicinity. These interfaces may have an extensive three dimensional structure as a result of biofilm formation. Organic molecules include carbon and energy sources, DNA, antibiotics, xenobiotics, quorum sensing chemicals, amino acids, proteins and enzymes. The movement and reactivity of these sorbed and sometimes more loosely associated structures are of great current interest as is the manipulation of these properties. For example, clay-associated extracellular DNA (arising from both natural and transgenic sources) may survive long enough to be transported by water through the soil profile or even taken up and incorporated into the genome of bacterial cells. Extracellular enzymes may retain their catalytic activity following adsorption to clays and humates: a property and a location that may have a significant impact on the degradation of organic macromolecules and the nutrient and energy dynamics of soil microroganisms. Associations of prions with clays can affect their migration and infectivity. We invite the submission of papers and posters that focus on the release of these diverse bio-chemicals by bacteria, fungi and plant roots and their extra-cellular locations and multiple functions in soil biology in relation to biodegradation processes, pathogenicity, gene transfer, plant nutrition, and the fate and behaviour of pollutants.

2.5.2 Bioavailability of metals and organics in soil

Bioavailability of metals and organics and their impact on soil and water quality

The bioavailability of potentially harmful organics and metals and their subsequent impact on microbes, plants, animals and humans as well as water quality is much researched. Measurements, definitions and the interpretation of bioavailability are controversial and often confusing but new research and ideas are moving us towards a resolution. The length of time which the xenobiotic is exposed to the soil (i.e. ageing) influences its chemical and physical state as well as its biological impact. Methods to assess the dynamics of sorption, desorption and other accumulation processes and to visualise the spatial relationship of the adsorbents and adsorbates to the soil biological components, have advanced in recent years. This symposium will emphasise new ideas concerning the processes and consequences of bioavailability and present ways in which surface associations can be manipulated in order to reduce undesirable impacts and to stimulate degradation and detoxification.