本研究では油圧ショベルの生産性の向上のための掘削制御方策の確立をシミュレーションモデルによって行い,その有効性の検証を行うことを目的とした.個別要素法を用いて土壌を離散的に解析することで,掘削の生産性を評価できるモデルを構築した.さらに油圧ショベルの動力学モデルを構築することで掘削作業を行うために必要なエネルギを解析する.この2つモデルを組み合わせ,掘削に必要なエネルギあたりの掘削量を生産性の指標として,生産性の定量的評価を行う. / 博士(工学) / Doctor of Philosophy in Engineering / 同志社大学 / Doshisha University

L'usage excessif de fertilisants azotés dans les pratiques agricoles modernes est préoccupant car il aboutit, entre autres, à la pollution des nappes phréatiques et à l’eutrophisation des eaux douces et marines. L’analyse du sol peut faciliter la mise en place de nouvelles pratiques agricoles qui tiennent davantage compte des variations temporelles et locales du sol et des plantes. Ces travaux visent donc le développement d’un système d’analyse in-situ, autonome et communicant pour le suivi en temps réel des teneurs en azote minéral du sol. Notre système est basé sur la technologie de microcapteur chimique en silicium lon-Sensitive Field Effect Transistor (ISFET). Une première phase de son développement a été dédiée à la fabrication de microcapteurs génériques pH-ISFET. La problématique de la détermination du pH du sol en insérant les pH-ISFET directement dans le sol a été considérée. Les résultats obtenus par cette méthode in-situ ont été comparés avec la méthode standard et nous avons examiné l’influence de paramètres propres au sol (humidité, texture, pH) et à l’ISFET (durée de vie, dérive temporelle). Dans un second temps, des puces pNH,-ISFET et pNO;-ISFET ont été obtenues en fonctionnalisant les puces génériques pH-ISFET grâce à l'intégration de membranes ionosensibles. La composition de ces membranes a été optimisée jusqu’à obtention de propriétés de détection (sensibilité, sélectivité, stabilité...) en adéquation avec les teneurs en ions ammonium et nitrates typiques des sols cultivés. Des premières caractérisations en conditions in-situ ont alors été effectuées. Finalement, les'capteurs ont été intégrés à un système permettant l’insertion des capteurs dans le sol, leur protection, l’alimentation électrique par batterie et la communication à distance des données de mesure. De premiers résultats, prometteurs, ont été obtenus. / Excessive use of nitrogen fertilizers in modern agricultural practices is a concern as it leads to groundwater pollution and eutrophication of fresh and marine waters. Soil testing can enable the introduction of new agricultural practices that take more into account temporal and local variations of soil and plants. This work therefore aims at the development of an in situ, autonomous and communicating analysis system for real-time monitoring of the mineral nitrogen contents of soils.Our system is based on the Ion-sensitive Field Effect Transistor (ISFET) microsensor technology. A first step of its development was dedicated to the fabrication of generic pH-ISFET microsensors. The problem of determining soil pH by inserting pH-ISFETs directly into the soil was considered. Results obtained by this in situ method were compared with the standard method and we examined the influence of soil ( moisture, texture, pH) and IFSET parameters (lifetime, time drift). In a second step, pNH4-ISFET and pNO3-ISFET chips were obtained by functionalizing the generic pH-ISFET chips with ionosensitive membrane. The composition of these membranes has been optimized until detection properties ( sensitivity, selectivity, stability, etc.) were in good accordance with the ammonium and nitrate ion contents of cultivated soils. Characterizations under in situ conditions were then carried out.Finally, the integration in the ground, the protection, the power supply and the remote communication of the sensors were made possible by the integration in a dedicated system. We obtained promising results.

Effective agricultural planning and environmental monitoring requires basic soil information. However, analyzing soil properties by conventional methods is often expensive and time consuming. In addition, these analyses result in chemical residues, which may be environmentally hazardous. In recent decades near-infrared diffuse reflectance spectroscopy (400-2500 nm) has been shown to be a viable alternative for rapidly analyzing soil properties. Information needs to be mathematically extracted from the spectra in order to correlate them with soil properties, and multivariate statistics are often used to calibrate soil prediction models.However, soils evaluated by the mid-IR region (4000 to 400 cm-1) warrants new studies. The primary aim of this study was to investigate the feasibility to use soil spectral data and chemometrics methods to predict soil properties, in order to reduce the number of conventional soil analyses. The understanding of the relationships between spectral characteristics and the physic-chemical properties of soils were evaluated in three different studies with soils of: (i) spectral library (Chapter 1), (ii) amazonian region (Chapter 2), (iii) soils contaminated with heavy metals and tannery sludge (Chapter 3).It was possible to identify regions of the vis-NIR and mid-IR spectra that showed absorption features due to water, iron oxides, and clay minerals. In Chapter 1 the predicted models for clay and soil organic matter showed high accuracy. It reflects the influence of the direct spectral responses of these properties in the NIR. The division of the large library into smaller subsets based on variation in the spectra characteristics was the best alternative to quantify soil attributes in tropical soils by Partial Least Square regressions. Another alternative would be to use Boosted regression trees for the whole library. In Chapter 2, the mid-IR predicted models outperformed the vis-NIR. Comparison of the interpolation results revealed that the predictions of the PLS regression (mid-IR and vis-NIR) adequately reproduced the spatial pattern of the properties evaluated, especially soil organic carbon and cation exchange capacity and, had the ability to predict the soil properties of unknown samples from a different geographical location. In Chapter 3, the metals adsorption to soil constituents caused expressive changes in soil spectral curves, showing spectral differentiation between highly contaminated soil and soils that are relatively contaminant-free. The results indicate that the Cr pseudo-total content can be predicted by spectroscopy reflectance with both sensors data. Fe and Mn also can be predicted accuratley by vis-NIR. The vis-NIR models outperformed the mid-IR. Besides these results, the vis-NIR instrument has less complicated sample and can be used directly in the field using portable spectrorradiometers. / Para o planejamento agrícola e o monitoramento ambiental são necessárias informações sobre os solos. As análises de solos realizadas através de métodos convencionais em laboratório são normalmente caras e demoradas. Além disso, geram resíduos químicos que caso não sejam dispostos e/ou tratados adequadamente, podem contaminar o ambiente. Nas últimas décadas a espectroscopia de reflectância difusa na região do visível e infravermelho próximo (vis-NIR, 400-2500 nm) do espectroeletromagnético tem se mostrado uma alternativa viável para analisar atributos de solo de maneira rápida. Para tanto, a informação espectral é matematicamente extraída do espectro e métodos multivariados são usados afim de correlacioná-la com as propriedades do solo. Entretanto, ainda são poucos estudos de solos em que a espectroscopia de reflectância na região do infravermelho médio (mid-IR, 4000-400 cm-1) foi usada. Objetivaram-se com este trabalho investigar a viabilidade da utilização de dados espectrais vis-NIR e mid-IR de solos e métodos quimiométricos para predizer as propriedades dos mesmos, a fim de reduzir o número de análises convencionais de terra. As relações existentes entre características espectrais e propriedades físico-químicas de solos tropicais foram avaliadas em três estudos distintos com solos (i) de uma biblioteca espectral (Capítulo 1), (ii) da região amazônica (Capítulo 2) e, (iii) contaminados com metais pesados e lodo de curtume (Capítulo 3). Foi possível identificar faixas espectrais nas regiões do vis-NIR e mid-IR relacionadas às feições de absorção características da água, óxidos de ferro e minerais de argila. No capítulo 1 os modelos de predição vis-NIR de argila e matéria orgânica do solo apresentaram elevada acurácia. Isto reflete a influência direta destas propriedades do solo na sua resposta espectral. A divisão da biblioteca espectral em subgrupos menores baseada nas características espectrais foi eficiente na quantificação de atributos de solos tropicais. Outra alternativa foi usar o método de regressão de árvores para o conjunto total de dados. No capítulo 2, os modelos de predição mid-IR foram mais precisos que os vis-NIR. Os modelos de carbono orgânico do solo e capacidade de troca catiônica obtidos pela regressão pelo método dos mínimos quadrados parciais permitiram a reprodução do padrão espacial destas propriedades na área estudada (r > 0.81); e puderam ser aplicados em uma área geográfica diferente, em amostras de solos desconhecidas. No capítulo 3, a adsorção de metais em constituintes dos solos provocou mudanças nas curvas espectrais dos mesmos, mostrando diferenças entre solos altamente contaminados por metais pesados e solos livres de contaminação. Os teores de Cr (semi-total) no solo pode ser predito através da espectroscopia de reflectância vis-NIR-mid-IR e regressão por mínimos quadrados parciais. Fe e Mn também foram preditos com acurácia usando dados vis-NIR. Em geral, os modelos de predição vis- NIR de metais pesados foram mais precisos que o mid-IR. A vantagem da utilização do sensor vis-NIR está no preparo mais simples de amostras e na possibilidade de utilizá-lo diretamente no campo.

Effective agricultural planning and environmental monitoring requires basic soil information. However, analyzing soil properties by conventional methods is often expensive and time consuming. In addition, these analyses result in chemical residues, which may be environmentally hazardous. In recent decades near-infrared diffuse reflectance spectroscopy (400-2500 nm) has been shown to be a viable alternative for rapidly analyzing soil properties. Information needs to be mathematically extracted from the spectra in order to correlate them with soil properties, and multivariate statistics are often used to calibrate soil prediction models.However, soils evaluated by the mid-IR region (4000 to 400 cm-1) warrants new studies. The primary aim of this study was to investigate the feasibility to use soil spectral data and chemometrics methods to predict soil properties, in order to reduce the number of conventional soil analyses. The understanding of the relationships between spectral characteristics and the physic-chemical properties of soils were evaluated in three different studies with soils of: (i) spectral library (Chapter 1), (ii) amazonian region (Chapter 2), (iii) soils contaminated with heavy metals and tannery sludge (Chapter 3).It was possible to identify regions of the vis-NIR and mid-IR spectra that showed absorption features due to water, iron oxides, and clay minerals. In Chapter 1 the predicted models for clay and soil organic matter showed high accuracy. It reflects the influence of the direct spectral responses of these properties in the NIR. The division of the large library into smaller subsets based on variation in the spectra characteristics was the best alternative to quantify soil attributes in tropical soils by Partial Least Square regressions. Another alternative would be to use Boosted regression trees for the whole library. In Chapter 2, the mid-IR predicted models outperformed the vis-NIR. Comparison of the interpolation results revealed that the predictions of the PLS regression (mid-IR and vis-NIR) adequately reproduced the spatial pattern of the properties evaluated, especially soil organic carbon and cation exchange capacity and, had the ability to predict the soil properties of unknown samples from a different geographical location. In Chapter 3, the metals adsorption to soil constituents caused expressive changes in soil spectral curves, showing spectral differentiation between highly contaminated soil and soils that are relatively contaminant-free. The results indicate that the Cr pseudo-total content can be predicted by spectroscopy reflectance with both sensors data. Fe and Mn also can be predicted accuratley by vis-NIR. The vis-NIR models outperformed the mid-IR. Besides these results, the vis-NIR instrument has less complicated sample and can be used directly in the field using portable spectrorradiometers. / Para o planejamento agrícola e o monitoramento ambiental são necessárias informações sobre os solos. As análises de solos realizadas através de métodos convencionais em laboratório são normalmente caras e demoradas. Além disso, geram resíduos químicos que caso não sejam dispostos e/ou tratados adequadamente, podem contaminar o ambiente. Nas últimas décadas a espectroscopia de reflectância difusa na região do visível e infravermelho próximo (vis-NIR, 400-2500 nm) do espectroeletromagnético tem se mostrado uma alternativa viável para analisar atributos de solo de maneira rápida. Para tanto, a informação espectral é matematicamente extraída do espectro e métodos multivariados são usados afim de correlacioná-la com as propriedades do solo. Entretanto, ainda são poucos estudos de solos em que a espectroscopia de reflectância na região do infravermelho médio (mid-IR, 4000-400 cm-1) foi usada. Objetivaram-se com este trabalho investigar a viabilidade da utilização de dados espectrais vis-NIR e mid-IR de solos e métodos quimiométricos para predizer as propriedades dos mesmos, a fim de reduzir o número de análises convencionais de terra. As relações existentes entre características espectrais e propriedades físico-químicas de solos tropicais foram avaliadas em três estudos distintos com solos (i) de uma biblioteca espectral (Capítulo 1), (ii) da região amazônica (Capítulo 2) e, (iii) contaminados com metais pesados e lodo de curtume (Capítulo 3). Foi possível identificar faixas espectrais nas regiões do vis-NIR e mid-IR relacionadas às feições de absorção características da água, óxidos de ferro e minerais de argila. No capítulo 1 os modelos de predição vis-NIR de argila e matéria orgânica do solo apresentaram elevada acurácia. Isto reflete a influência direta destas propriedades do solo na sua resposta espectral. A divisão da biblioteca espectral em subgrupos menores baseada nas características espectrais foi eficiente na quantificação de atributos de solos tropicais. Outra alternativa foi usar o método de regressão de árvores para o conjunto total de dados. No capítulo 2, os modelos de predição mid-IR foram mais precisos que os vis-NIR. Os modelos de carbono orgânico do solo e capacidade de troca catiônica obtidos pela regressão pelo método dos mínimos quadrados parciais permitiram a reprodução do padrão espacial destas propriedades na área estudada (r > 0.81); e puderam ser aplicados em uma área geográfica diferente, em amostras de solos desconhecidas. No capítulo 3, a adsorção de metais em constituintes dos solos provocou mudanças nas curvas espectrais dos mesmos, mostrando diferenças entre solos altamente contaminados por metais pesados e solos livres de contaminação. Os teores de Cr (semi-total) no solo pode ser predito através da espectroscopia de reflectância vis-NIR-mid-IR e regressão por mínimos quadrados parciais. Fe e Mn também foram preditos com acurácia usando dados vis-NIR. Em geral, os modelos de predição vis- NIR de metais pesados foram mais precisos que o mid-IR. A vantagem da utilização do sensor vis-NIR está no preparo mais simples de amostras e na possibilidade de utilizá-lo diretamente no campo.

Abstract There are various after-use options on the cut-away peatlands, depending on the characteristics of the soil. If the soil is devoid of rock, cultivation of reed canary grass is a profitable after-use option. The aim of this study was to determine how characteristics of peat, peatland surroundings and fertilizers influence the element uptake of reed canary grass. In the present investigation the peat production areas of Luesuo, Piipsanneva and Jouttenisenneva were selected as study areas. A comprehensive sampling programme was carried out in each of the study areas. In addition, two experimental areas for cultivation of reed canary grass were established in Luesuo and Hankilanneva between 2004 and 2005. The results obtained indicate that all study areas were suitable for cultivating reed canary grass, but fertilizers must be added to make up nutrient deficiencies. The study areas were very clean from heavy metals. The results also suggest that the characteristics of peat or surroundings of peatland do not influence the nutrient level of peat significantly, considering the cultivation of reed canary grass. The large geochemical provinces have a smaller impact on nutrient and heavy metal levels in the peat on the peat cut-away areas compared to smaller geochemical units. Heavy metal content in the peat and in the mineral soil under the peat seems to correlate. Reed canary grass does not uptake heavy metals from the cultivation media effectively. Liming slag was better for liming in cultivation of reed canary grass than ash. Although ash has large amounts usable nutrients, especially potassium, it did not raise the heavy metal content in peat to harmful levels, it can therefore be used in the cultivation of reed canary grass. Stock fertilized fur animal manure compost produced almost as much biomass as optimized artificial fertilizers. After the correction of nutrient deficiencies, compost is suitable for the cultivation of reed canary grass in peatlands. Because the total nutrient levels are high in compost, its fertilizer effect lasts longer than in artificial fertilizers, where nutrients are all in a dissolved form. Already in the first growing season the cultivation of reed canary grass changed the cut-away peatland from a carbon source to a carbon sink. In this respect, the reed canary grass cultivation can be used to produce bioenergy to replace fossil fuels in accordance with the goals of Kyoto Protocol. / Tiivistelmä Turvetuotannosta vapautuneella suopohjalla toteutetaan erilaisia jälkikäyttötapoja riippuen suopohjan ominaisuuksista. Jos suopohja on kohtuullisen kivetöntä, ruokohelpiviljely on kannattavaa. Viljelty ruokohelpi poltetaan turpeen tai hakkeen seassa. Tämän tutkimuksen tarkoitus oli selvittää miten pohjaturpeen ja suopohjan ympäristöalueiden ominaisuudet sekä viljelyyn käytetyt lannoite- ja kalkitusaineet vaikuttavat ruokohelpin käyttämiin ravinteisiin. Ruokohelpiviljelyn lannoituskustannukset ovat suuret, joten suopohjan luontainen ravinnetila kannattaa huomioida lannoitusta suunniteltaessa. Suopohjan ravinnetila saadaan selville laatimalla alueelle viljavuusanalyysi. Kyseisen analyysin yhteydessä on hyödyllistä tehdä myös raskasmetallianalyysit, jotta viljelykäyttöön tulevan suopohjan puhtaudesta voidaan varmistua. Tutkimuksen kohdealueiksi valittiin Luesuon, Piipsannevan ja Jouttenisennevan turvetuotantoalueet. Lisäksi tutkimusta varten perustettiin ruokohelpin viljelykoealueet Luesuolle ja Hankilannevalle vuosina 2004 ja 2005. Tutkimusalueilla suoritettiin kattava näytteenotto. Näytteistä analysoitiin tärkeimmät kasviravinteet sekä joukko raskasmetalleja. Tulosten perusteella tutkimusalueille laadittiin viljavuusluokittelu. Tutkimusalueet soveltuvat hyvin ruokohelpiviljelyyn, mutta ravinnepuutokset tulee korjata lannoituksella käytettäen suopohjille suositeltua lannoitusta. Tutkimusalueet osoittautuivat puhtaiksi raskasmetalleista. Tutkimuksen kohteina olleiden suopohjien liukoisen kaliumin ja fosforin pitoisuudet olivat hyvin alhaisia, eivätkä turpeen tai ympäristön ominaisuudet vaikuttaneet niiden pitoisuuksiin ruokohelpiviljelyn kannalta merkittävästi. Liukoisen magnesiumin ja kalsiumin pitoisuudet sen sijaan vaihtelivat tutkituilla suopohjilla kohtuullisen paljon riippuen turpeen ominaisuuksista. Geokemiallisella provinssilla ei todettu olevan niin suurta merkitystä suopohjien lopputurpeiden alkuainepitoisuuksiin kuin pienemmillä geokemiallisilla yksiköillä. Tutkittujen suopohjien turpeen ja sen alla olevan kivennäismaan raskasmetallipitoisuudet korreloivat keskenään. Tutkimustulosten mukaan kasvualustan raskasmetallit eivät siirry tehokkaasti ruokohelpiin. Poikkeuksena olivat sinkin ja molybdeenin pitoisuudet, joita ruokohelpissä esiintyi korkeampina pitoisuuksina kuin kasvualustassa. Haitallisten raskasmetallien pitoisuudet olivat huomattavasti alhaisempia ruokohelpissä kuin kasvualustassa. Ruokohelpi sisälsi raskasmetalleja erittäin pieninä pitoisuuksina, joten viimeisen kasvukuukauden muutokset olivat vaikeasti tulkittavissa. Näyttää kuitenkin siltä, että ruokohelpi siirtää ainakin osan kuparista, sinkistä ja molybdeenistä juuristoonsa talven ajaksi. Suoritettujen lannoituskokeiden perusteella teräskuona soveltuu voimalaitostuhkaa paremmin turvekentän kalkitukseen ruokohelpiviljelyssä. Voimalaitostuhka sisältää kuitenkin huomattavia määriä hyödynnettäviä ravinteita, etenkin kaliumia. Tutkimuksessa havaittiin, ettei voimalaitostuhka lisännyt edes ylisuurina annoksina kasvualustan raskasmetallipitoisuuksia haitallisesti, joten sitä voidaan käyttää ruokohelpiviljelyssä. Varastolannoitetulla kompostilla saavutettiin lähes yhtä hyvä ruokohelpisato kuin optimoidulla mineraalilannoitteella. Näin ollen turkislantakompostia voidaan ravinnekorjausten jälkeen käyttää mainiosti ruokohelpiviljelyyn. Kompostin ravinnevaikutus on myös suurten kokonaisravinnepitoisuuksien vuoksi pidempi kuin mineraalilannoitteilla. Fosforin varastolannoitus turkislantakompostilla onnistui ensimmäisen kasvukauden perusteella hyvin. Tutkimuksessa todettiin, että jo ensimmäisenä kasvukautena ruokohelpiviljelyllä saadaan muutettua hiililähteenä toimiva entinen turvetuotantoalue hiilinieluksi. Ruokohelpiviljelyllä tuotetulla bioenergialla voidaan lisäksi korvata fossiilisia polttoaineita Kioton ympäristösopimuksen tavoitteiden mukaisesti.

Most soil particles loses cohesion and split up the soil mass into individual soil grains when they come in contact with water and get saturated. In dispersive soils the particles detach more spontaneously from each other and go into suspension even in quiet water. Thus the phenomenon of dispersion is common to most soils, the degree varying from soil to soil. Dispersive soils are abundantly found in various parts of the world such as Thailand, United States, Australia, Mexico, Brazil, South Africa and Vietnam. Several geotechnical failures such as piping due to internal erosion, erosion and gullying in relatively flat areas, collapse of sidewalls and topsoil removal have been reported worldwide due to the construction in dispersive soil. Failures as reported could be prevented if such soils are identified before-hand or if the quantification of dispersivity in the soil is done accurately. There are several methods of measuring dispersivity in soils which include several physical tests, chemical tests and some common laboratory tests. It is reported in literature that no method could be completely relied upon to identify dispersive soils with absolute confidence. In addition, when these methods were studied in detail, several flaws surfaced needing a better estimation of dispersivity. In order to develop a new method of estimation of dispersivity, the mechanism of dispersion in soils was studied in depth, which revealed that the existing concepts regarding dispersivity are incomplete in many aspects. An exhaustive philosophy of dispersion which addresses every detail is non-existing. To solve these problems, the concept of dispersivity was investigated in detail. It was found out that the observed dispersivity is a result of repulsion in the soil overcoming the attractive force. Thus a list of factors that could possibly affect the repulsion and attraction (and hence the dispersivity) in soils were found out. Even though literature focuses on exchangeable sodium as the principal reason for dispersivity, from fundamental theoretical considerations several other factors such as Cation exchange capacity (CEC), pH, structure of the soil, electrolyte concentration in the pore fluid, presence of organic matter, clay minerals involved in the soil and dissolved salts in the soil could possibly have an influence on dispersivity. Several studies have reported soils of high dispersivity to possess a high pH, high CEC, high amounts of sodium. The influence of these factors on dispersivity of other soils (or generally in any soil) is not well explored. Research on understanding their mechanism of action led to the conclusion that these parameters could be generalized for any soil. Through the analysis of these parameters, it was found that the fundamental parameter governing the dispersivity of soils is the number of charges on clay particles and that the repulsion in the soils is mainly contributed by the electrostatic repulsion. The attractive force in a soil/clay mass is primarily contributed by the van der Waal’s attraction and dispersion occurs when the electrostatic repulsion (resulting due to permanent and pH dependent charges) dominates over the van der Waal’s attraction. A practical estimation of charge with least effort could be possibly carried out through the measurement of zeta potential of soils. In order to verify whether the effect of all the factors is completely and sufficiently reflected in the zeta potential values, experiments were conducted on various soils. Three soils namely Suddha soil (a locally available dispersive soil), Black cotton soil and Red soil were selected for the study. These soils were chosen as the soil samples as they could display wide ranges of dispersivity values. In order to perform dispersivity tests, soil fraction finer than 75µ (75 micron meter sieve size) was fixed as the sample size as dispersivity pertaining to the finer fractions play a greater role than that of the coarser particles. All the three soil samples were treated with sodium hydroxide and urea solutions to alter the dispersivity so that the influence of all parameters could be studied. The dispersivity of the treated and untreated soils was found out through the various conventional tests and it was found that there exists a good correlation between the dispersivity and the zeta potential of soils. It was also observed that the increase in the dispersivity is higher when treated with salts of monovalent cations. Increase in the organic content also increased zeta potential, but not as significantly. One of the popularized theories on colloidal dispersions is the classical DLVO theory which has formulated the total interaction energy of colloidal particles by estimating the electrostatic repulsion and van der Waal’s attraction energy between two particles. The total interaction energy is then expressed as the difference between them. A similar approach as taken by the DLVO is adopted in this study. The total attractive energy existing in a soil mass is mathematically derived from the expression for van der Waal’s energy between two particles and the total repulsive energy from the zeta potential values. Two different approaches namely an infinitesimal particle approach and a finite particle approach is taken for finding the energy in a soil mass. In the infinitesimal particle approach, a clay particle is assumed to be infinitely small such that any soil particle of a finite radius could be conceived to be formed by a combination of infinite number of these infinitesimal particles. With this setting, the total energy in a soil mass is computed without really bothering about what exact particles constitute the mass. The increase in energy due to the increase in radius is then integrated to obtain the final expression. The dispersivity of the soil is then estimated under defined physical conditions of the soil. In the finite particle approach, each particle is considered to be of finite radius and to estimate the total energy, the total number of particle ombinations is then taken and the total energy is expressed as a sum of all the possible combinations. The dispersivity of a soil in both approaches is expressed as a release of energy when the repulsion rules over the attraction. In order to validate the derived propositions and expressions, experiments were conducted again on soils. The soils were treated with hydroxide salt of monovalent cations such as lithium, sodium and potassium. The dispersivity of the various treated and untreated soils was measured with the conventional methods and with the derived expressions of dispersivity through zeta potential. The similarity in the trend of the dispersivity values confirmed the validity of the derived expression. It was also concluded that the infinitesimal particle approach could be adopted when information about the physical properties are available and when they are not, the finite approach could be used. An accurate determination of zeta potential is critical for representation of dispersivity with zeta potential. Thus the procedure for measurement of zeta potential was standardized. The standardization was primarily focused on establishing the ideal conditions for zeta potential measurement. The role of Brownian motion, in electrophoretic mobility measurements were studied by employing the usage of zeta deviations. Untreated, potassium hydroxide treated, sodium hydroxide treated and lithium hydroxide treated samples of Suddha soil, Black Cotton soil and Red soil (finer than 75µ) were used for the study. Zeta potential measurements on unfiltered soil water suspensions, suspensions passing 2.5µ and suspensions passing 0.45µ were conducted along with recording their zeta deviations. It was observed that soil suspensions finer than 0.45µ show acceptable values of zeta deviations and thus could be used as a standard procedure for estimating zeta potentials. It was also concluded that the presence of Brownian motion makes the assessment of zeta potential through electrophoretic measurements easier and accurate. In an alternate perspective it as deduced that the amount of total monovalent ion concentration in the soil (dissolved and adsorbed) could adequately serves as an ideal parameter that could be used to quantify dispersion in soils. In order to verify the speculation, the variation of repulsive pressure with monovalent cation concentration was studied for the above mentioned treated and untreated soils. Within the monovalent cations, the role of ionic size in repulsion along with physical factors was also studied with the help of Atterberg limits, compaction characteristics, and dispersivity measurements. It could be concluded that even though there are several chemical factors such as CEC, pH, electrolyte concentration, type of clay minerals, dissolved salts etc. and physical factors such as plasticity, water holding capacity, density and structure which influence dispersion in soils, these factors affect either directly forces between the particles or the surface charge of clays which again affect the forces. The two phenomena can be combined through the hydration behaviour of the adsorbed cations on the clay surface in view of dispersivity. It is that force due to hydration which acts as the principal reason to separate the clay particles apart. As the radius of the inner hydration shell is higher for monovalent cations than those of higher valency ions, more force would be offered by the monovalent ions. Higher the charge and higher is the number of monovalent cations, higher will be the repulsion and thus the dispersivity. The repulsive force offered by the monovalent cations in soil was calculated through osmotic pressure differences and the dispersivity was expressed as the release of energy as earlier. In order to validate the proposal, the dispersivity of the samples as measured with the conventional methods was compared and studied with the derived expression. The similarity in the trend of the dispersity values confirmed the validity of the derived expressions. Thus, it can be seen that there are primarily two different methods of quantifying dispersivity of soils. When one method estimates dispersivity by calculating the electrostatic repulsion through zeta potential, the other method gives a dispersivity value based on the repulsive pressure offered by the monovalent cations in the soil. Two methods could be regarded as two different measurements of the electrical double layer. Any method could be used based on the property that could be easily quantified. The applicability of the new approaches – calculation of monovalent cations and zeta potential- for estimating the dispersivity in soils through a complete development of philosophy of dispersion and is presented, in this thesis, in nine chapters as follows: In Chapter 1 the background of the study and review of literature connected with the present study is presented. The mechanism of dispersion and the geotechnical problems associated with dispersion is elaborately presented in this section. As the dispersive soils cannot be identified through conventional tests, a description about the various tests designed to identify dispersive soils is presented. Earlier works relevant to the topic and the shortcomings of those studies are discussed. Finally, the objectives of the current research along with the scope of the work are explained in the concluding part of this chapter. Various factors that could have influence on the dispersivity of soils and their mechanism of action are presented in Chapter 2. The relationship of the factors with zeta potential is discussed. Theories dealing with dispersivity, conventional methods of measurement, role of geotechnical characteristics in assessing dispersivity are being presented. Chapter 3 deals with the various materials and methods used for the study. A locally available dispersive soil called Suddha soil along with Black Cotton soil and Red soil were chosen as the soils for the study of dispersion. The basic material properties and testing programs adopted for the study are presented in this chapter. The codal procedures followed to determine the physical, chemical, index and engineering properties are described in detail. The experimental investigations carried to bring out the role of zeta potential in dispersivity of soils are described in Chapter 4. Detailed analysis of the results showed estimation of zeta potential is possible and can sufficient quantify dispersivity of soils. The formulation of the equation for estimating dispersivity from zeta potential is described in Chapter 5. The estimation dispersivity based on attraction and repulsion energies in a soil mass is presented here. The adoption of the approach and methodologies used based on classical DLVO theory for the current work is explained in detail. The values of dispersivity obtained from the derived equation are compared with those obtained from the conventional tests. The validity of the expression is confirmed with the results of the experiments. Chapter 6 deals with the standardization of the measurement procedure of zeta potential. Role of Brownian motion in the accurate measurement of electrophoretic mobilities are brought out here. Chapter 7 brings out an alternate perspective of quantifying dispersivity through monovalent cations. The role of monovalent cations and the mechanism in which they contribute to the repulsive pressures (hence the dispersivity) are discussed. Experimental research design adopted has brought that the effect of monovalent and ionic size on repulsive pressures leading to dispersivity is described. The results of the experiments added with the inferences drawn are explained at the end. The estimation of repulsive pressures for measuring dispersivity from monovalent cations is discussed in Chapter 8. The dispersivity of a soil mass is derived from monovalent ion concentration and experiments were carried out for verification purposes. The experimental investigation procedure adopted followed by the results are presented in this chapter. It was observed that a good co-relation exists with the dispersivity obtained from the monovalent ion concentration and that obtained from conventional methods. Chapter 9 compares the dispersivity obtained through the various methods proposed in this thesis. The comparison is made in light of the classical electrical double layer theory. The major conclusions of the study are brought out at the end of this chapter.

In der Landnutzung stellt die Bewertung der Versorgung mit organischer Bodensubstanz (OBS) eine besondere Herausforderung dar. Dabei wird der Einfluss der Bodenfeuchte aufgrund des globalen Klimawandels an Bedeutung gewinnen, da die Wasserverfügbarkeit Einfluss auf die Aktivität der bodenlebenden Mikroorganismen nimmt. Ziel der Arbeit waren daher Aussagen, inwieweit verschiedene Wassergehalte den biologischen Umsatz bei der Inkubation von Bodenproben mit unterschiedlicher Herkunft sowie organischer Düngung beeinflussen. In einem Modellversuch wurden Bodenproben ungedüngter Parzellen von drei deutschen Dauerfeldversuchen in einer zweifaktoriellen Blockanlage in Abhängigkeit von organischer Düngung (Weizenstroh, Stallmist) und Wassergehalt inkubiert. Die Experimente wurden in vier Feuchtigkeitsstufen mit 10, 40, 65 und 90 % der Feldkapazität über einen Zeitraum von 85 Tagen bei einer Temperatur von 25 °C realisiert. Zusätzlich sind vor und nach der Inkubation Thermogravimetrische Bodenanalysen (TGBA) durchgeführt worden. Die Ergebnisse belegen einen mit dem Wassergehalt steigenden C-Umsatz, da die Aktivität von aeroben Mikroorganismen bis zur Wassersättigung des Bodens zunimmt. Die Steigerung war bei Zugabe von Weizenstroh höher als bei Stallmist, ohne Düngerzusatz signifikant niedriger. Gleichzeitig änderte sich die Dynamik der Abbauprozesse. Durch besonders trockene Verhältnisse wurde die Umsetzung verzögert, zudem sank die Umsatzrate langsamer. Ein dauerhafter Einfluss des Standorts auf den Umsatz der Düngemittel war dagegen nicht nachweisbar. Der biologische Abbau im Inkubationsversuch veränderte darüber hinaus die thermische Zerfallsdynamik. Die größten Veränderungen wurden nach Zugabe von Stroh festgestellt. Nicht geklärt werden konnte, ob in Böden mit höherer Versorgung durch organische Substanz gleiche Ergebnisse erzielt werden können. / In land use, the assessment of the supply of organic soil matter (OBS) is a particular challenge. The influence of soil moisture on global climate change will become increasingly important, as water availability influences the activity of soil-living microorganisms. The aim of the work is therefore to determine the extent to which different water contents influence the biological turnover during the incubation of soil samples with different origins as well as organic fertilisation. In a model experiment, soil samples from unfertilized plots of three German long-time field experiments were incubated in a two-factor block facility depending on organic fertilization (wheat straw, manure) and water content. The experiments were carried out in four humidity levels with 10, 40, 65 and 90 % of the field capacity over a period of 85 days at a temperature of 25 °C. In addition, thermogravimetric soil analyses (TGBA) were performed before and after incubation. The results prove a C turnover increasing with the water content, since the activity of aerobic microorganisms increases until the water saturation of the soil. The increase was higher with the addition of wheat straw than with manure, without fertilizer significantly lower. At the same time, the dynamics of the degradation processes changed. Due to particularly dry conditions, conversion was delayed and the turnover rate fell more slowly. A lasting influence of the site on fertilizer turnover was not proved. In addition, the biological degradation in the incubation experiment changed the thermal decay dynamics. The largest changes were observed after the addition of straw. It could not be clarified whether the same results could be achieved in soils with a higher supply of organic matter.