Background: Soil microbes are key drivers of carbon (C) and nutrient cycling in terrestrial ecosystems, and their properties are influenced by the relationship between resource demand and availability. - Aims: Our objective was to investigate patterns of microbial properties and their controls to understand whether they differ between soils derived from geochemically contrasting parent material in tropical montane forests. - Methods: We measured microbial biomass C (MBC/Soil), potential extracellular enzyme activity (pEEA), and assessed microbial investments in C and nutrient acquisition at the beginning and end of a 120-day laboratory incubation experiment using soils developed from three geochemically contrasting parent material (i.e., mafic, mixed sediment, and felsic) and three soil depths (0–70 cm). - Results: We found that MBC/Soil and pEEA were highest in soils developed from the mafic parent material. Microbial investment in C acquisition was highest in soils developed from mixed sedimentary rocks and lowest in soils developed from the felsic parent material. We propose that our findings are related to the strength of contrasting mineral-related C stabilization mechanisms and varying C quality. No predominant microbial investment in nitrogen (N) acquisition was observed, whereas investment in phosphorus (P) acquisition was highest in subsoils. We found lower microbial investment in C acquisition in subsoils indicating relatively high C availability, and that microbes in subsoils can substantially participate in C cycling and limit C storage if moisture and oxygen conditions are suitable. Geochemical soil properties and substrate quality were important controls on MBC/Soil per unit soil organic C (MBC/SOC), particularly after the exhaustion of labile and fast cycling C, that is, at the end of the incubation. - Conclusion: Although a laboratory incubation experiment cannot reflect real-world conditions, it allowed us to understand how soil properties affect microbial properties. We conclude that parent material is an important driver of microbial properties in tropical montane forests despite the advanced weathering degree of soils.

La sfida nel 21esimo secolo è quella di fornire cibo e energia ad un mondo in continua crescita demografica e allo stesso tempo conservare l’ambiente. In questa tesi uno scenario alternativo di uso del suolo per la produzione di bioenergia è stato testato: le fasce tampone bioenergetiche. Considerate le problematiche ambientali legate al trilemma “cibo-energia-ambiente”, la struttura del Millennium Ecosystem Assessment sui servizi ecosistemici (SE) fornisce l’opportunità di esaminare l’impatto ambientale di questo nuovo scenario bioenergetico. In questa tesi ho mirato a determinare in che misura le colture bioenergetiche poliennali influenzino la fornitura multipla di SE quando coltivate come fasce tampone. Per raggiungere questo obiettivo, ho combinato una revisione sistematica della letteratura sui SE forniti da colture energetiche poliennali (CEP) con una prova sperimentale su fasce tampone bioenergetiche. Applicando una metodologia di attribuzione di punteggi agli impatti sui SE estratti dal materiale bibliografico raccolto, ho mostrato come coltivando le CEP lungo i margini dei campi coltivati esista una grande opportunità per sostenere la fornitura multipla di SE. La coltivazione delle CEP come fasce tampone adiacenti a campi agricoli può migliorare i SE di regolazione del clima, dell’acqua e della biodiversità, sostenere la salute del suolo e fornire biomassa dedicata alla produzione di bioenergia. Al contrario, la conversione di margini di campo di prati stabili ha mostrato un impatto netto negativo sulla fornitura multipla di SE. Tuttavia, due sono i principali svantaggi che sono stati individuati relativamente alla creazione e alla gestione delle fasce tampone bioenergetiche. Primo, diversi sono i fattori sito-specifici di tipo idro-pedologico lungo i margini dei campi che devono essere tenuti in considerazione poiché possono avere un impatto negativo sull’affrancamento delle colture e la loro produttività a medio-lungo termine. Secondo, riguardo la catena di approvvigionamento della biomassa, uno spazio di lavoro limitato per le macchine agricole è stato riconosciuto come principale inconveniente per le fasce tampone bioenergetiche rispetto alle CEP coltivate in pieno campo. Questo limite logistico di natura spaziale può inevitabilmente incrementare i tempi e le operazioni di taglio e raccolta della biomassa e quindi in ultima il consumo di combustili fossili. Grazie ad una prova sperimentale su fasce tampone bioenergetiche condotta in un terreno sabbioso-limoso con falda acquifera poco profonda contaminata da nitrati di origine agricola, si è dimostrato come fasce tampone coltivate con miscanto e salice siano in grado di intercettare e rimuovere i nitrati in falda (>60%) tanto quanto fasce tampone con specie avventizie. CEP come miscanto e salice, grazie ai loro apparati radicali profondi, hanno mostrato essere in grado di promuovere delle relazioni pianta-suolo-microorganismi lungo l’intero profilo del suolo utili ai fini ambientali delle fasce tampone bioenergetiche. Infatti, negli strati più profondi, una maggiore biomassa radicale ha portato le CEP a superare le specie avventizie in termini di rimozione biologica dei nitrati dal suolo e mitigazione potenziale dei gas serra. Inoltre, i risultati relativi alla produzione di biomassa e le asportazioni di N legata alla fase di raccolta hanno confermato ulteriormente come la coltivazione di CEP lungo i corsi d’acqua sia una strategia win-win: produzione di biomassa e protezione dell’ambiente. In conclusione, il potenziale rivelato dalle CEP in termini di fornitura multipla di SE suggerisce che la loro coltivazione, come elementi paesaggistici perenni in posizioni strategiche all'interno di paesaggio agricolo, è un'opzione promettente per promuovere l'intensificazione ecologicamente sostenibile degli agroecosistemi. / The 21st century will challenge agriculture to feed and fuel a growing world while conserving the environment. In this thesis an alternative bioenergy land use scenario to the conversion of marginal land has been tested: the bioenergy buffers. Given the environmental issues related to “food-energy-environment” trilemma, the Millennium Ecosystem Assessment framework on ES provides an opportunity to examine the environmental impacts of this new bioenergy land use scenario. In this thesis I aimed to determine to what extent do the perennial bioenergy crops affect the delivery of multiple ES when cultivated as bioenergy buffers. To reach this aim, I combined a systematic revision of literature on ES provided by perennial bioenergy crops with a field experiment on bioenergy buffers. Applying an impact scoring methodology to the effects on ES extracted from literature, I showed that, cultivating perennial bioenergy crops along field margins of former croplands offer a great opportunity to sustain the provision of multiple ES. The cultivation of perennial bioenergy crops on field margins can improve climate, biodiversity and water regulation services, sustain soil health and provide biomass for energetic purposes. On the contrary, grassland conversion showed a net negative impact on multiple ES provision. Nevertheless, I found two main shortcomings related to bioenergy buffers establishment and management. First, several site-specific factors along field margins must be taken into account, because they can affect crop establishment and buffers long-term productivity. Second, regarding to biomass supply chain, a limited working space for the farm machinery operations has been recognized as the main disadvantages of bioenergy buffers compared to large-scale bioenergy plantations. This spatial logistics constraint may inevitably increase harvest and collection operation times and fossil fuel consumption. Conducting a field experiment with bioenergy buffers in a nitrate-enriched shallow groundwater, I showed that miscanthus and willow buffers are able to efficiently intercept and remove from groundwater the incoming NO3-N as much as buffer strips with spontaneous species. Yet, due to their deep rooting systems, bioenergy buffers promote significant plant-microbial linkages along the soil profile. At deeper soil layers, a higher fine root biomass led perennial bioenergy crops to outperform patches of adventitious vegetation in terms of biological N removal from soil and belowground GHG mitigation potential. The results on biomass production and N removal via harvesting further confirmed that the cultivation of perennial bioenergy crops along watercourses is an effective win-win strategy: biomass production and protection of the environment. In conclusion, the revealed potential of perennial bioenergy crops on multiple ES provision implies that their cultivation as perennial landscape elements in strategic locations within landscape is a promising option to promote the ecological sustainable intensification of agroecosystems.

Une mauvaise connaissance des propriétés des sols et de leur fonctionnement peut avoir de nombreuses conséquences néfastes sur le rendement et la qualité des récoltes, sur la dégradation des sols et sur une pollution de l’environnement. En raison de l’importance des pratiques agricoles, notre étude s’est focalisée sur leur impact sur la qualité et la santé des sols. La recherche s’est effectuée de novembre 2003 à octobre 2007 sur des vergers de pommiers implantés sur des collines dans le nord-est de la Slovénie. Deux pratiques agricoles fréquentes dans cette région ont été suivies : (i) une irrigation localisée au goutte à goutte sur des Calcaric Cambisol (CALCOSOL) développés sur marnes, et ses effets sur la stabilité structurale des sols et leur biomasse microbienne à la Station expérimentale de Gačnik et (ii) la combinaison d’un engrais organique (Compo guano) et d’un amendement calcaire dans un verger conduit en agriculture biologique à Pohorski dvor sur un District Cambisol (ALOCRISOL) développé sur schistes. La présence de microbes pathogènes fécaux dans le sol, dus à l’irrigation ou à l’apport d’engrais organiques animaux a aussi été recherchée sur les deux sites. Le régime hydrique du sol a été suivi durant deux étés par des relevés tensiométriques hebdomadaires sur les deux sites. A la station expérimentale de Gačnik, un rang irrigué a été comparé à un rang non irrigué. La teneur en matière organique totale, son fractionnement granulométrique et la signature isotopique des différentes fractions permettant de discuter de leur origine et leur turn over ont été mesurés. La biomasse microbienne et son activité ont été caractérisées au printemps et à l’automne en 2004 et 2005. La stabilité structurale a été mesurée selon la méthode de Bartoli à l’automne 2004 et au printemps 2005. Sur le verger conduit en agriculture biologique à Pohorski dvor seul le pH et les paramètres microbiologiques ont été suivis selon la même périodicité en comparant les différents traitements dans une expérimentation par blocs. Enfin, sur les deux sites, une quantification des champignons, des bactéries (aérobies, anaérobies, coliformes fécaux) et des virus présents dans le sol a été réalisée. Incidence de l’irrigation par goutte à goutte sur la qualité du sol sur le site de Gačnik sur la qualité physique du sol- Les sols de ce verger, argilo-limoneux et carbonatés, varient fortement de l’amont à l’aval de la parcelle située sur une pente de 15%. le sol est peu épais à l’amont, la marne altérée apparaissant dès 60 cm tandis qu’à mi-pente et à l’aval le sol est épais >1 m et la marne plus fortement altérée. L’observation des profils pédologiques et l’historique de la parcelle montrent que le sol a été fortement remanié sur les 60 premiers centimètres préalablement à la plantation du verger. Le passage d’une plantation en terrasses à une plantation dans le sens de la pente a conduit à l’effacement des terrasses suivi d’un labour profond dont en voit encore la trace à 60 cm de profondeur à l’aval de la parcelle (Fig. 3.3 & Tab. 3.9). Un échantillonnage systématique de la teneur en carbone organique de l’horizon de surface, selon un pas de 6 m, montre un accroissement selon la pente suivant une forme en zig-zag reflétant la trace des anciennes terrasses (Fig. 3.19). Dans les 30 premiers centimètres la teneur en matières organiques, le rapport C/N et la capacité d’échange cationique augmentent de l’amont vers l’aval tandis la teneur en carbonates de calcium décroît (Fig. 3.15). Le pH reste stable entre 8 et 8, 4. A la surface du sol dans les rangs de plantation traités par désherbage chimique, une croûte alguaire se forme sur le côté ombragé du rang... / Underestimation of soil properties and poor understanding of soil conditions can have many negative consequences, which results in quality or quantity of yield, soil degradation or even environmental pollution. According to importance of agricultural practices, our study focused on their impact on soil quality and health. The research took place from November 2003 to October 2007 in apple orchards in north-eastern Slovenia where two frequent agricultural practices were investigated: (i) drip irrigation on Calcaric Cambisol and its effects on structural stability and microbial biomass at Gačnik experimental station and (ii) combination of organic fertiliser (Campo guano) and liming in organic farming to enhance microbial biomass and nitrogen nutrition at Pohorshi dvor on Dystric Cambisol. The presence of faecal pathogens in the soil due to irrigation or organic fertilizer was also investigated. Water potential was measured during two seasons in both locations. Structural stability according Bartoli method, organic mater characteristics (including grain size organic matter fractionation and isotopic signature of organic carbon origin), and microbiological parameters were analysed as potential indicators of soil quality in irrigation practice comparing an irrigated (IR) to a non-irrigated (NIR) row. In organic farming, mainly pH and microbiological parameters were followed according treatments on an experimental blocks comparison. According to hilly terrain and land levelling in Gačnik, we were dealing with two groups of soil differing in thickness, organic matter, and calcium carbonate contents: one at upslope and another at mid and downslope. Considering soil characteristics, slope effect was more expressed than irrigation effect. According to slope, water gravimetric content (W), organic matter (OM), microbial biomass (MB), and respiration (R) increased towards downslope while total carbonates (Ca) and structural stability (SS) decreased. According to irrigation, W, OM, and SS contents decreased, while MB and R increased from NIR to IR rows. No difference was observed for Ca between treatments. According to slope, higher carbonate content was as an important factor for higher structural stability as organic matter pool. According to irrigation, lower W in IRR row could be explained by modification in root distribution due to drip irrigation. Irrigation leads to an increase of soil microbial biomass and its activity (as a short-time effect) and decrease of OM (as a long-term effect); moreover, a decrease of OM originating from the marl bedrock was observed in IRR row and attributed to microbial mineralization. Lower SS of IRR row is related to the OM reduction. Seasonal variations of structural stability show complex trends resulting from the combination of climatic conditions and biological activity. In organic fertilising study, the interaction of Compo guano and lime together was not clear, but in long term this is probably the best solution because it had positive consequences on both soil pH and available nitrogen, while preserving fair levels of MB and labile organic matter (LOM). Irrigation water and Compo guano were considered as eventual sources of faecal coliforms which remains in soils. From our study it was concluded that OM, MB, R and faecal coliforms can be treated as general useful indicators in assessing soil quality. According to agricultural practice, SS should be emphasized as an important quality indicator in irrigation practice and pH in organic farming.

Submitted by Jorge Silva (jorgelmsilva@ufrrj.br) on 2016-08-17T18:27:17Z No. of bitstreams: 1 2000 - Pedro Nilson Alves Berto.pdf: 654186 bytes, checksum: ef66a21a2e6b0ca326c348f84fb13d3e (MD5) / Made available in DSpace on 2016-08-17T18:27:17Z (GMT). No. of bitstreams: 1 2000 - Pedro Nilson Alves Berto.pdf: 654186 bytes, checksum: ef66a21a2e6b0ca326c348f84fb13d3e (MD5) Previous issue date: 2000-12-12 / CHAPTER I: In a Inceptisol soil, at Santa Cruz Sugar Mill, Campos dos Goytacazes/RJ, an experiment was conducted with the purpose to evaluate, during the cycle of second ratoon answers to the application of sugarcane agroindustry wastes, in consitions of harverst management with and without previous burning, using the growth quantitative analysis and utilizing the RB72454 sugarcane variety. The experimental field was planted in April 1992. The plant cane cut ocurred in July 1993. The first ratoon was harvested in August 1994, when the test was reinstalled to evaluation in the second ratoon, which harvest was in September 1995. The tested treatment were: 1 = CC = raw cane; 2 ? CC + TF = raw cane + 30 t.ha-1 of filter cake; 3 ? CC + TF + B = raw cane + 20 tons of filter cake ha-1 + 10 t.ha-1 of bagasse; 4 ? CQ = burned cane; 5 ? CQ + TF = burned cane + 30 t.ha-1 of filter cake; 6 ? CQ + TF + B = burned cane + 20 t.ha-1 of filter cake + 10 t.ha-1 of bagasse. The physiological rates discussed and interpreted were: a) Number of stalks by linear meter; b) Stalk height (m); c) Total biomass (g.m-2 soil); d) Leaf area index (m2 leaf. m-2 soil); e) Growth tax of the cultural (g.m-2 leaf. day-1); f) Liquid assimilation tax (g.m-2 leaf.day-1); g) Leaf nitrogen concentration; h) Stalk nitrogen concentration. The results allowed the following conclusions: 1) The application of the sugar agroindustry wastes (filter cake and bagasse) in areas harvest with or without burning, didn?t increased the stalks number and canes height. 2) The fact of not have significant differences to the stalks number rates by linear meters and canes height, reflected directly in a not statistical difference among the evaluated treatments, beeing relative a industrial stalks final productivity in t.ha. 3) The value of total biomass, obtained in the various treatments, was very low, mainly in function of hydric deficit ocurred in the period of the development of the experiment. 4) O I.A.F. (leaf area index), showed little significant changes in the first samples (second, fourth and sixth months), with higher values to burning treatments, in function of a higher stalks number by meter found in this parcels. 5) The straw index calculated (20, 6 t.ha-1) affected the ratoon budding, lowing the stalks population. 6) The leaf area index stayed lower than that considered ideal to the development of a productive sugarcane plantation, correlating with the law productivity obtained, beeing a good physiological parameter to the estimation of a sugarcane?s production. 7) The growth tax of the culture showed the highest values between 120 e 240 days after cut, similar to all treatments during the vegetative development cycle and coincided to the highest foliar area index. 8) The liquid assimilation tax was affected by the hydric stress in the period of the maximum growth of the culture. 9) The nitrogen leafs concentration, as the nitrogen stalks concentration didn?t show differences among the treatments. The fact that the soil studied was a Inceptisol soil, with great natural fertility and that ocurred a great hydric stress during the culture cycle, may have equalized the answers. -------------------------------------------------------------------- CHAPTER II: In a Inceptisol soil of Santa Cruz sugar mill; located at Campos dos Goytacazes,RJ, an experiment was conducted to evaluate the influence, in the chemical and biological properties of the soil, during the sugar cane second ratoon, of the sugar industry wastes (filter cake and bagasse) applied into experimental parcels harvested with and without previous burning of the cane. The experimental field was planted in April 1992. The harvest of the cane ocurred in July 1993. The first 1994, ratoon was harvested in August when the experiment was reinstalled for evaluation in the second ratoon, which harvest was done in September 1995. The tested treatments were: 1= CC= raw cane; 2- CC+TF= raw cane + 30 t.ha -1 of filter cake; 3-CC+TF+B= raw cane + 20 tons of filter cake ha-1 + 10 t. ha-1 of bagasse; 4-CQ= burned cane; 5- CQ +TF= burned cane + 30 t ha-1 of filter cake; 6-CQ + TF + B= burned cane + 20 t.ha-1 of filter cake + 10 T.ha-1 of bagasse. The parameters discussed and interpreted were: a) manufacturable stalks productivity in t.ha-1; b) Sugar production in t Pol ha -1; c) microbial soil biomass-carbon in mgCg -1 of soil; d) agroindustrial wastes effect among treatments on the productivity of second and the third curts of the in t.sugarcane ha-1; e) treatments effects on soil chemical properties; f)straw index determination. The results allowed the following conclusions: 1- The application of the sugar agroindustry wastes (filter cake and bagasse), in the sugar cane fields harvested with or without burning, didn`t result in increasing of productivity, in t.ha-1 or in t.ha-1. 2- Raw cane treatments, that received industrial wastes, showed expressive higher values of BMS-C, in comparison with burned cane treatments, mainly in raw cane treatment with filter cake. 3- The Inceptisol soil, may have facilitaded the similarity of the production results (t cane ha-1), due to the its high natural fertility. 4- Straw index, equivalent to 20,6 t. straw ha, may have affected the ratoon budding of the raw cane treatments. 5- generally speaking, the soil chemical properties studied haven`t been modified when the treatments are compared. / CAP?TULO I: Em solo Cambissolo eutr?fico, da usina Santa Cruz, RJ, foi conduzido experimento objetivando avaliar, durante ciclo de segunda soca (terceiro corte da cultura da cana-de-a??car), respostas ? aplica??o de res?duos da agroind?stria a?ucareira, em condi??es de manejo de colheita com e sem pr?via queima, utilizando-se da an?lise quantitativa de crescimento e empregando-se a variedade RB72454. O campo experimental foi plantado no m?s de abril de 1992. O corte da cana-planta ocorreu em julho de 1993. A primeira soca foi colhida em agosto de 1994, ocasi?o em que se reinstalou o ensaio para avalia??o na Segunda soca ou terceiro corte, cuja colheita aconteceu em setembro de 1995. Os tratamentos efetuados foram: 1 ? CC = cana-crua; 2 ? CC + TF = cana crua + 30 toneladas. ha-1 de torta de filtro; 3 ? CC + TF + B = cana-crua + 20 toneladas de torta de filtro . ha-1 + 10 toneladas . ha-1 de baga?o; 4 ? CQ = cana queimada; 5 ? CQ + TF = cana queimada + 30 toneladas . ha-1 de torta de filtro; 6 ? CQ + TF + B = cana queimada + 20 toneladas . ha-1 de torta de filtro + 10 toneladas . ha-1 de baga?o. Os par?metros fisiol?gicos discutidos e interpretados foram: a) n?mero de colmos por metro linear; b) altura do colmo (m); c) fitomassa total (g.m-2 solo); d) ?ndice de ?rea foliar (m2 folha . m-2 solo); c) taxa de crescimento da cultura (g. m- 2 solo.dia-1); f) taxa de assimila??o l?quida (g.m-2 folha.dia-1); g) concentra??o de nitrog?nio nas folhas; h) concentra??o de nitrog?nio no colmo. Os resultados obtidos permitiram as seguintes conclus?es: 1. A aplica??o dos res?duos da agroind?stria a?ucareira (torta de filtro e baga?o), nas ?reas colhidas com e sem queima, n?o resultou em aumento no n?mero de colmos por metro linear e nem na altura das canas. 2. O fato de n?o haver diferen?as significativas para os par?metros n?mero de colmos por metro linear e de altura das canas, refletiu-se diretamente na n?o diferen?a estat?stica entre os tratamentos avaliados, no que se refere ? produtividade final dos colmos industrializ?veis em t.ha-1. 3. O valor da fitomassa total, obtida nos diversos tratamentos, apresentou-se muito baixo, em fun??o principalmente do d?ficit h?drico ocorrido no per?odo de condu??o do experimento. 4. O I.A.F. (?ndice de ?rea foliar), apresentou varia??es significativas nas primeiras amostragens (segundo, quarto e sexto meses), com valores maiores para os tratamentos com queima, em fun??o de maior n?mero de colmos por metro encontrado nestas parcelas. 5. O ?ndice de palhi?o calculado (20,6 t.ha-1) afetou a brota??o de soqueiras dos tratamentos com cana crua, prejudicando a popula??o de colmos. 6. O ?ndice de ?rea foliar ficou abaixo do considerado ideal para a forma??o de lavoura produtiva, correlacionando-se com a baixa produtividade obtida, mostrando-se como um bom par?metro fisiol?gico para estimativa da produ??o canavieira. 7. A taxa de crescimento da cultura apresentou valores m?ximo entre 120 e 240 dias ap?s o corte, foi semelhante para todos tratamentos ao longo do ciclo de desenvolvimento vegetativo e coincidiu com os per?odos de ?ndice de ?rea foliar m?ximos. 8. A taxa de assimila??o l?quida foi afetada pelo estresse h?drico no per?odo de m?ximo crescimento da cultura. 9. A concentra??o de nitrog?nio nas folhas, assim como a concentra??o de nitrog?nio nos colmos, n?o apresentou diferen?as entre tratamentos. O fato de o solo estudado ser um Cambissolo eutr?fico, com alta fertilidade natural e de ter ocorrido forte stress h?drico durante o ciclo da cultura, pode ter nivelado as respostas. -------------------------------------------------------------------- CAP?TULO II: Num Cambissolo eutr?fico da usina Santa Cruz, localizada no munic?pio de Campos dos Goytacazes, RJ, foi conduzido experimento objetivando avaliar, durante ciclo de segunda soca (terceiro corte) da cultura da cana-de-a??car, o efeito de res?duos da fabrica??o do a??car, (torta de filtro e baga?o), aplicados em parcelas experimentais posteriormente colhidas com cana crua e com cana sem queima, nas suas propriedades qu?micas e biol?gicas. O campo experimental foi plantado no m?s de abril de 1992. O corte da cana-planta ocorreu em julho de 1993. A primeira soca foi colhida em agosto de 1994, ocasi?o em que se reinstalou o ensaio para avalia??o na segunda soca ou terceiro corte, cuja colheita aconteceu em setembro de 1995. Os tratamentos efetuados foram: 1 ? CC = cana crua; 2 ? CC + TF = cana crua + 30 toneladas.ha-1 de torta de filtro; 3 ? CC + TF + B = cana crua + 20 toneladas de torta de filtro.ha-1 + 10 toneladas.ha-1 de baga?o; 4 ? CQ = cana queimada; 5 ? CQ + TF = cana queimada + 30 toneladas .ha-1 de torta de filtro; 6 ? CQ + TF + B = cana queimada + 20 toneladas.ha-1 de torta de filtro + 10 toneladas.ha-1 de baga?o. Os par?metros discutidos e analisados foram: a) produtividade de colmos industrializ?veis em t.ha-1; b) produ??o de a??car em t POL.ha-1; c) biomassa microbiana do solo-carbono em mgC.g-1 de solo; d) efeito dos res?duos agroindustriais entre tratamentos, nas produtividades dos segundo e terceiro cortes, em t cana.ha-1; e) efeito dos tratamentos sobre as propriedades qu?micas do solo; f) determina??o do ?ndice do ?palhi?o?. Os resultados obtidos permitiram as seguintes conclus?es: 1 ? A aplica??o dos res?duos da agroind?stria a?ucareira (torta de filtro e baga?o), nos canaviais colhidos com e sem queima, n?o resultou em aumentos de produtividade, quer seja em t cana.ha-1 ou em t pol.ha-1. 2 ? Os tratamentos com cana crua que receberam res?duos industriais, apresentaram valores significativamente maiores de BMS-C, em compara??o ao tratamento cana queimada. Houve uma maior propor??o de carbono imobilizado na biomassa microbiana do solo, principalmente no tratamento cana crua com torta de filtro adicionada. 3 ? O tipo de solo estudado, Cambissolo Eutr?fico, pode ter facilitado a semelhan?a dos resultados de produ??o (t cana.ha-1), em fun??o de sua alta fertilidade natural. 4 ? O ?ndice de Palhi?o, equivalente a 20,6 t.ha-1 de palha, pode ter afetado a brota??o de soqueiras dos tratamentos com cana crua. 5 ? De modo geral, as propriedades qu?micas do solo estudadas n?o foram alteradas quando se compararam os tratamentos.

The fate of the carbon and nitrogen in dairy farm effluent (DFE) applied onto soil was investigated through laboratory experiments and field lysimeter studies. They resulted in the development and testing of a complex carbon (C) and nitrogen (N) simulation model (CaNS-Eff) of the soil-plant-microbial system. To minimise the risk of contamination of surface waters, regulatory authorities in New Zealand promote irrigation onto land as the preferred treatment method for DFE. The allowable annual loading rates for DFE, as defined in statutory regional plans are based on annual N balance calculations, comparing N inputs to outputs from the farming system. Little information is available, however, to assess the effects that these loading rates have on the receiving environment. It is this need, to understand the fate of land-applied DFE and develop a tool to describe the process, that is addressed in this research. The microbially mediated net N mineralisation from DFE takes a central role in the turnover of DFE, as the total N in DFE is dominated by organic N. In a laboratory experiment, where DFE was applied at the standard farm loading rate of 68 kg N ha⁻¹, the net C mineralisation from the DFE was finished 13 days after application and represented 30% of the applied C, with no net N mineralisation being measured by Day 113. The soluble fraction of DFE appeared to have a microbial availability similar to that of glucose. The low and gradually changing respiration rate measured from DFE indicated a semi-continuous substrate supply to the microbial biomass, reflecting the complex nature and broad range of C compounds in DFE. The repeated application of DFE will gradually enhance the mineralisable fraction of the total soil organic N and in the long term increase net N mineralisation. To address the lack of data on the fate of faecal-N in DFE, a ¹⁵N-labelled faecal component of DFE was applied under two different water treatments onto intact soil cores with pasture growing on them. At the end of 255 days, approximately 2% of the applied faecal ¹⁵N had been leached, 11 % was in plant material, 11 % was still as effluent on the surface, and 40% remained in the soil (39% as organic N). Unmeasured gaseous losses and physical losses from the soil surface of the cores supposedly account for the remaining ¹⁵N (approximately 36%). Separate analysis of the total and ammonium nitrogen contents and ¹⁵N enrichments of the DFE and filtered sub-samples (0.5 mm, 0.2µm) showed that the faecal-N fraction was not labelled homogeneously. Due to this heterogeneity, which was exacerbated by the filtration of DFE on the soil surface, it was difficult to calculate the turnover of the total faecal-N fraction based on ¹⁵N results. By making a simplifying assumption about the enrichment of the ¹⁵N in the DFE that infiltrated the soil, the contribution from DFE-N to all plant available N fractions including soil inorganic N was estimated to have been approximately 11 % of the applied DFE-N. An initial two-year study investigating the feasibility of manipulating soil water conditions through controlled drainage to enhance denitrification from irrigated DFE was extended a further two years for this thesis project. The resulting four-year data set provided the opportunity to evaluate the sustainability of DFE application onto land, an extended data set against which to test the adequacy of CaNS-Eff, and to identify the key processes in the fate of DFE irrigated onto soil under field conditions. In the final year of DFE irrigation, 1554 kg N ha⁻¹ of DFE-N was applied onto the lysimeters, with the main removal mechanism being pasture uptake (700 kg N ha⁻¹ yr⁻¹ removed). An average of 193 kg N ha⁻¹ yr⁻¹ was leached, with 80% of this being organic N. The nitrate leaching decreased with increasing soil moisture conditions through controlled drainage. At the high DFE loading rate used, the total soil C and N, pH and the microbial biomass increased at different rates over the four years. The long-term sustainability of the application of DFE can only be maintained when the supply of inorganic N is matched by the demand of the pasture. The complex simulation model (CaNS-Eff) of the soil-plant-microbial system was developed to describe the transport and transformations of C and N components in effluents applied onto the soil. The model addresses the shortcomings in existing models and simulates the transport, adsorption and filtration of both dissolved and particulate components of an effluent. The soil matrix is divided into mobile and immobile flow domains with convective flow of solutes occurring in the mobile fraction only. Diffusion is considered to occur between the micropore and mesopore domains both between and within a soil layer, allowing dissolved material to move into the immobile zone. To select an appropriate sub-model to simulate the water fluxes within CaNS-Eff, the measured drainage volumes and water table heights from the lysimeters were compared to simulated values over four years. Two different modelling approaches were compared, a simpler water balance model, DRAINMOD, and a solution to Richards' equation, SWIM. Both models provided excellent estimation of the total amount of drainage and water table height. The greatest errors in drainage volume were associated with rain events over the summer and autumn, when antecedent soil conditions were driest. When soil water and interlayer fluxes are required at small time steps such as during infiltration under DFE-irrigation, SWIM's more mechanistic approach offered more flexibility and consequently was the sub-model selected to use within CaNS-Eff. Measured bromide leaching from the lysimeters showed that on average 18% of the bromide from an irrigation event bypassed the soil matrix and was leached in the initial drainage event. This bypass mechanism accounted for the high amount of organic N leached under DFE-irrigation onto these soils and a description of this bypass process needed to be included in CaNS-Eff. Between 80 and 90% of the N and C leached from the lysimeters was particulate (> 0.2 µm in size), demonstrating the need to describe transport of particulate material in CaNS-Eff. The filtration behaviour of four soil horizons was measured by characterising the size of C material in a DFE, applying this DFE onto intact soil cores, and collecting and analyzing the resulting leachate using the same size characterisation. After two water flushes, an average of 34% of the applied DFE-C was leached through the top 0-50 mm soil cores, with a corresponding amount of 27% being leached from the 50-150 mm soil cores. Most of the C leaching occurred during the initial DFE application onto the soil. To simulate the transport and leaching of particulate C, a sub-model was developed and parameterised that describes the movement of the effluent in terms of filtering and trapping the C within a soil horizon and then washing it out with subsequent flow events. The microbial availability of the various organic fractions within the soil system are described in CaNS-Eff by availability spectra of multiple first-order decay functions. The simulation of microbial dynamics is based on actual consumption of available C for three microbial biomass populations: heterotrophs, nitrifiers and denitrifiers. The respiration level of a population is controlled by the amount of C that is available to that population. This respiration rate can vary between low level maintenance requirements, when very little substrate is available, and higher levels when excess substrate is available to an actively growing population. The plant component is described as both above and below-ground fractions of a rye grass-clover pasture. The parameter set used in CaNS-Eff to simulate the fate of DFE irrigated onto the conventionally drained lysimeter treatments over three years with a subsequent 10 months non-irrigation period was derived from own laboratory studies, field measurements, experimental literature data and published model studies. As no systematic calibration exercise was undertaken to optimise these parameters, the parameter set should be considered as "initial best estimates" and not as a calibrated data set on which a full validation of CaNS-Eff could be based. Over the 42 months of simulation, the cumulative drainage from CaNS-Eff for the conventionally drained DFE lysimeter was always within the 95% CI of the measured value. On the basis of individual drainage bulking periods, CaNS-Eff was able to explain 92% of the variation in the measured drainage volumes. On an event basis the accuracy of the simulated water filled pore space (WFPS) was better than that of the drainage volume, with an average of 70% of the simulated WFPS values being within the 95% CI for the soil layers investigated, compared to 44% for the drainage volumes. Overall the hydrological component of CaNS-Eff, which is based on the SWIM model, could be considered as satisfactory for the purposes of predicting the soil water status and drainage volume from the conventionally drained lysimeter treatment for this study. The simulated cumulative nitrate leaching of 4.7 g NO₃-N m⁻² over the 42 months of lysimeter operation was in good agreement to the measured amount of 3.0 (± 2.7) g NO₃-N m⁻². Similarly, the total simulated ammonium leaching of 2.7g NH₄- N m⁻² was very close to the measured amount of 2.5 (± 1.35) g NH₄- N m⁻² , however the dynamics were not as close to the measured values as with the nitrate leaching. The simulated amount of organic N leached was approximately double that measured, and most of the difference originated from the simulated de-adsorption of the dissolved fraction of organic N during the l0-month period after the final DFE irrigation. The 305 g C m⁻² of simulated particulate C leached was close to the measured amount of 224 g C m⁻² over the 31 months of simulation. The dissolved C fraction was substantially over-predicted. There was good agreement in the non-adsorbed and particulate fractions of the leached C and N in DFE. However, the isothermic behaviour of the adsorbed pools indicated that a non-reversible component needed to be introduced or that the dynamics of the de-adsorption needed to be improved. Taking into account that the parameters were not calibrated but only "initial best estimates", the agreement in the dynamics and the absolute amounts between the measured and simulated values of leached C and N demonstrated that CaNS-Eff contains an adequate description of the leaching processes following DFE irrigation onto the soil. The simulated pasture N production was in reasonable agreement with the measured data. The simulated dynamics and amounts of microbial biomass in the topsoil layers were in good agreement with the measured data. This is an important result as the soil microbial biomass is the key transformation station for organic materials. Excepting the topsoil layer, the simulated total C and N dynamics were close to the measured values. The model predicted an accumulation of C and N in the topsoil layer as expected, but not measured. Although no measurements were available to compare the dynamics and amounts of the soil NO₃-N and NH₄-N, the simulated values appear realistic for an effluent treatment site and are consistent with measured pasture data. Considering the large amount of total N and C applied onto the lysimeters over the 42 months of operation (4 t ha⁻¹ of N and 42 t ha⁻¹0f C), the various forms of C and N in dissolved and particulate DFE as well as in returned pasture, and that the parameters used in the test have not been calibrated, the simulated values from CaNS-Eff compared satisfactorily to the measured data.

In the present thesis, implications of pasture establishment, fertilization and abandonment on soil C and nutrient dynamics were investigated for the mountain rainforest region of southern Ecuador. Over the past decades the natural forest of the study area has been threatened by conversion to cattle pastures. However, the soil fertility of these extensively grazed pastures (active pastures) declines continuously during pasture use. The invasion of bracken fern (Pteridium arachnoideum) leads to pasture abandonment when bracken becomes dominant. In order to reveal the mechanisms behind the deterioration of soil fertility, biotic and abiotic soil properties and their interaction were analyzed along a land‐use gradient (natural forest – active pasture – abandoned pasture). The ecosystem disturbance of the mountain rainforest through pasture use changed the microbial function and structure, and affected soil CO2‐C fluxes. Annually, 2 Mg soil CO2‐C ha‐1 were additionally emitted from the pasture land. This acceleration in soil respiration rates was related to accelerated rates of microbial C mineralization and fine‐root respiration. The high‐quality, N‐rich above‐ and belowground residues of the pasture grass (S. sphacelata, C4‐plant), especially the huge fine‐root biomass, provided a high C and N availability for soil microbes. Compared to the forest, increased soil pH and accelerated base saturation were further factors beneficial for soil microbial growth and metabolism of the upper mineral soil at active pastures. Three times higher amounts of microbial biomass C and a significant shift in the microbial community structure towards a higher relative abundance of Gram(‐)‐ bacteria and fungi were observed. Long‐term pasture use and the invasion of bracken (C3‐plant) diminished beneficial effects for microbes, causing a significant decrease in the C, net, and gross N mineralization rates as well as a two‐third reduction in the microbial biomass. A preferential substrate utilization of grass‐derived C4 by the soil microbes resulted in a rapid decline of the C4‐pool. As a consequence, the less available C3‐pool from bracken and former forest increased its dominance in the SOC‐pool, further decreasing pasture productivity and finally causing pasture abandonment. The lower quality and quantity of above‐ and belowground residues of the bracken (high lignin content, C/N) resulted in resource‐limited conditions that influenced the microbial function to greater extent than their structure. The microbial structure seemed to be sensitive mainly to soil pH along the land‐use gradient. Thus, a disconnection between microbial structure and function was identified. Fertilization experiments were conducted both in the lab and in the field to evaluate the impact of urea and/or rock phosphate amendment on SOM dynamics and on pasture productivity of active pastures. After combined fertilization the pasture yield was most efficiently increased by 2 Mg ha−1 a−1, indicating a NP‐limitation of grass growth. Furthermore, the fodder quality was improved by a higher content of P and Ca in the grass biomass. The microorganisms of the active pasture soil responded with an adaptation of their structure to the increased substrate availability in the short term, but did not change their initial functions in the long term. After urea/ rock phosphate addition a significant increase in the relative fungal abundance was detected, but neither a microbial limitation of energy nor of N or P was observed. However, urea addition accelerated gaseous losses of soil CO2‐C in the short term. In the study area, pronounced alterations in ecosystem functioning due to land‐use changes were detected, especially in soil C and N cycling rates. For a sustainable land‐use in this region it is crucial to prevent pasture degradation and to rehabilitate degraded pastures in order to protect the prevailing mountain rainforest ecosystem. It is of crucial importance for active pasture soils to maintain or even increase resource availability, being one indicator of soil fertility. In this context, the soil organic matter has to be retained in the long‐term to maintain high microbial activity and biomass, and thus pasture productivity. A moderate fertilization with urea and rock phosphate can be a first step to provide continuous nutrient supply for grass growth and to strengthen livestock health through increased fodder quality. However, the risk of further additional emissions of soil CO2‐C due to increased loads of urea fertilizer application has to be kept in mind. Overall, for the establishment of a sustainable land‐use management the control of bracken invasion and an adjusted nutrient management are needed. Further investigations on the reduction of soil nutrient losses and increased nutrient use efficiencies of plants, such as combined planting with legumes or the usage of cultivars with special nutrient acquisition strategies, should be in the focus of future work. / In der vorliegenden Dissertation werden die Auswirkungen der Weideetablierung, ‐düngung sowie des Verlassens von Weiden auf Bodenkohlenstoff‐ und Nährstoffdynamik in einer tropischen Bergregenwaldregion Ecuadors zusammenfassend dargestellt und diskutiert. Der Naturwald des Untersuchungsgebietes ist seit Jahrzehnten durch Brandrodung und die Umwandlung in extensiv genutztes Weideland (aktive Weide) in seinem flächenhaften Bestand bedroht. Als Problem hat sich der Verlust an Fruchtbarkeit der Weideböden während ihrer Bewirtschaftung herausgestellt. Des Weiteren führt die Einwanderung des Tropischen Adlerfarns (Pteridium arachnoideum, C3‐Pflanze) zu einer Reduktion der oberirdischen Grasbiomasse. Nimmt diese Entwicklung überhand, werden die betroffenen Flächen von den Bauern nicht mehr aktiv genutzt, verlassen und neuer Regenwald gerodet. Um mehr über die Mechanismen der Verringerung der Bodenfruchtbarkeit zu erfahren, wurden biotische und abiotische Bodeneigenschaften und deren Interaktion entlang eines Landnutzungsgradienten (Naturwald – aktive Weide – verlassene Weide) untersucht. Die Zerstörung des Bergregenwaldökosystems und die Überführung der gerodeten Flächen zur Weidebewirtschaftung verändert die Funktion und Struktur der Bodenmikroorganismen und beeinflusst den CO2‐C Fluss aus dem Boden. Jährlich werden 2 t CO2‐C ha‐1 zusätzlich vom Weideland emittiert. Diese Erhöhung der Bodenatmungsraten kann mit erhöhten Raten der mikrobiellen C‐Mineralisierung und Feinwurzelatmung in Verbindung gebracht werden. Das Weidegras (S. sphacelata, C4‐Pflanze) liefert C‐ und N‐reiche ober und unterirdische organische Substanz (z.B. durch die Feinwurzelbiomasse) und trägt damit zu einer Erhöhung der C‐ und N‐Verfügbarkeit für die mikroorganismen bei. Darüber hinaus stellen ein höherer pH‐Wert und eine erhöhte Basensättigung im oberen Mineralboden der aktiven Weide günstige Bedingungen für mikrobielles Wachstum und Metabolismus dar. Als Konsequenz sind die Gehalte an mikrobiellem Biomassekohlenstoff um das Dreifache erhöht und die mikrobiellen Gemeinschaftsstrukturen signifikant in Richtung einer höheren relativen Abundanz der Gram(‐)‐Bakterien und Pilze verschoben. Eine längerfristige Weidebewirtschaftung ohne Kompensation von Nährstoffverlusten sowie die Einwanderung des Tropischen Adlerfarnes verschlechterte die Bedingungen für die Mikroorganismen, was zu einem signifikanten Rückgang des SOC, der Netto‐ und Brutto‐N‐Mineralisierungsraten sowie zu einer Halbierung der mikrobiellen Biomasse führt. Eine bevorzugte Substratnutzung von Graskohlenstoff (C4) durch die Mikroorganismen hat einen schnellen Abbau des C4‐Pools zur Folge. Somit dominiert nun der mikrobiell schlechter verfügbare C3‐Pool den Bodenkohlenstoffpool. Dies führt zu einem weiteren Rückgang der Weideproduktivität und schließlich zum Offenlassen der Weide. Die geringere Qualität und Quantität der vom Farn stammenden ober‐ und unterirdischen organischen Substanz (hoher Ligninanteil, weites C/N), führten zu einer Limitierung der Ressourcen für die Mikroorganismen, welche deren Funktionen in größerem Maße beeinflussen als deren Gemeinschaftsstruktur. Im Gegensatz dazu wird entlang des Landnutzungsgradienten die Struktur hauptsächlich durch den pH‐Wert beeinflusst. Daraus folgt, dass Struktur und Funktion der Bodenmikroorganismen voneinander entkoppelt auf Veränderungen reagieren können. Um den Einfluss von Harnstoff‐ und/ oder Rohphosphatdüngung aktiver Weiden auf die Dynamik der organischen Bodensubstanz und auf die Weideproduktivität zu untersuchen, wurden sowohl Labor‐ als auch Feldversuche durchgeführt. Im Feldexperiment wurde gezeigt, dass eine NP‐Limitierung der Grasbiomasseproduktion vorliegt und durch eine geringe NP‐Kombinationsdüngung die oberirdische Phytomasseproduktion um 2 t ha−1 a−1 gesteigert und die Futterqualität durch eine Erhöhung der P‐ und Ca‐ Gehalte verbessert werden kann. Die Mikroorganismen reagierten mit einer Anpassung ihrer Struktur an die kurzzeitig erhöhte Substratverfügbarkeit. Nach Gabe von Harnstoff und/ oder Rohphosphat wurde weder eine N‐ noch eine P‐Limitierung der Bodenmikroorganismen festgestellt, und die mikrobiellen Funktionen wurden langfristig nicht verändert. Dagegen bewirkte die Düngergabe einen erhöhten relativen Anteil der Pilzabundanz. Im Labor sowie im Feld kam es nach Harnstoffdüngung kurzzeitig zu verstärkten gasförmigen Verlusten des Bodenkohlenstoffs. Aufgrund der Landnutzungsänderungen im Untersuchungsgebiet veränderten sich die Ökosystemfunktionen stark, speziell die Boden‐C‐ und Boden‐N‐Umsatzraten. Für eine nachhaltige Landnutzung in der Region, d. h., für den Schutz der noch verbliebenen natürlichen Bergregenwaldflächen, ist es von entscheidender Bedeutung, dass die Weidedegradierung verhindert wird und degradierte Flächen wieder in Nutzung genommen werden. Als entscheidend für die Weideproduktivität hat sich in dieser Studie die Ressourcenverfügbarkeit für Bodenmikroorganismen herausgestellt. Daher ist es sehr wichtig, diese Ressourcenverfügbarkeit in Böden aktiv‐genutzter Weiden zu erhalten oder noch zu erhöhen, denn sie wirkt sich vor allem auf die organische Bodensubstanz und im Wechselspiel damit auf die mikrobielle Biomasse und Aktivität aus. Eine moderate Kombinationsdüngung aus Harnstoff und Rohphosphat ist ein erster Schritt in diese Richtung. Dabei sollte jedoch das Risiko zusätzlicher bodenbürtiger CO2‐C Emissionen in Folge höherer Düngergaben berücksichtigt werden. Für ein nachhaltiges Landnutzungsmanagement sind Maßnahmen gegen die Einwanderung des Adlerfarnes und ein angepasstes Nährstoffmanagement notwendig. Weitere Untersuchungen sollten auf eine Minimierung der Nährstoffverluste und eine erhöhte Nährstoffnutzungseffizienz der Pflanzen fokussiert werden. Weidemischkulturen aus Gräsern mit Leguminosen sowie der Einsatz von Kulturen mit speziellen Nährstoffaneignungsstrategien könnten dabei eine große Rolle spielen und sollten in der Region erprobt werden. / La tesis presentada investiga el impacto del establecimiento de pasto, de su fertilización y de su manejo tradicional (abandono del pastizal) a la dinámica del carbono y de los nutrientes de suelo en la región de los bosques tropicales montañosos en el Sur de Ecuador. Durante las últimas décadas el bosque natural en el área de estudio ha estado amenazada por su conversión a pastizales. Sin embargo, la fertilidad del suelo en pastos de tipo extensivo (pastos activos) decrece frecuentemente durante el uso de los pastos. La invasión de Llashipa (Pteridium arachnoideum) conduce al abandono de los pastos cuando la ésta se vuelve dominante. Con la finalidad de revelar los mecanismos detrás de esta disminución de la fertilidad de suelo, se analizaron las propiedades bióticas y abióticas del suelo y sus interacciones, a lo largo de una gradiente del uso de la tierra (bosque natural —pasto activo — pastos abandonados). La perturbación del ecosistema de bosque tropical montañoso por su cambio de uso, mediante el establecimiento de pastizales, ha alterado la función y la estructura de los microorganismos y ha afectado el flujo de CO2‐C del suelo. Cada año 2 Mg CO2‐C ha‐1 fueron emitidas adicionalmente por el establecimiento de pastos. Esta aceleración en la tasa de respiración del suelo está relacionada con el aumento de las tasas de mineralización microbiana de carbono y de la respiración de las raíces. La alta calidad y abundancia de N de los residuos orgánicos del suelo con pasto Mequeron (S. sphacelata, C4‐planta), especialmente debido a la gran biomasa de las raíces finas, ofrecen una disponibilidad alta de C y N para los microorganismos. En comparación con el bosque natural, el aumento del pH y la saturación bases acelerada fueron condiciones más favorables para el crecimiento microbiano y para el metabolismo microbiano en el parte superior del suelo mineral en pastos activos. La cantidad de C de la biomasa de los microorganismos fue tres veces mayor que la del bosque y se ha observado un cambio significativo de la estructura de la comunidad microbiana, en donde la abundancia relativa de los hongos y de las bacterias Gram(‐) ha aumentado. El uso de pasto a largo plazo y la invasión de Llashipa (C3‐planta) han reducido los efectos benéficos para los microorganismos, que resultaron en una reducción significativa de las tasas de la mineralización de C y N, y en una reducción en dos tercios de la biomasa microbiana. El uso preferencial de los microorganismos por sustrato de pasto C4 han resultado en una rápida disminución de la reserva de C4. Como consecuencia, la menor disponibilidad de la reserva de C3 de las plantas de Llashipa y de la cobertura anterior de bosque ha incrementado su dominancia en la reserva de materia orgánica del suelo. Eso resulta, en una mayor disminución de la productividad de los pastos, conduciendo finalmente al abandono de los campos de pastos. La menor calidad y cantidad de los residuos acumulados sobre y bajo el suelo provenientes de la Llashipa han dado como resultado un sustrato de limitadas condiciones que están afectando más a las funciones microbiales antes que a su estructura. La estructura microbiana parece ser más sensible al pH del suelo a largo de la gradiente del uso de la tierra; de manera que se ha identificado una desconexión entre la estructura y función microbial. Experimentos de fertilización en laboratorio y en campo han sido realizados para evaluar el impacto de la aplicación de enmiendas (urea y/o roca fosfórica) a la dinámica de la materia orgánica y a la productividad de los pastos activos. El resultado del experimento de campo ha demostrado que la fertilización combinada es más efectiva, mostrando un aumento en la producción de biomasa de 2 Mg ha−1 a−1, lo que indica una limitación de N y P para el crecimiento del pasto. Además, la calidad de forraje se mostró incrementada ya que el contenido de P y de Ca han aumentado significativamente. Los microorganismos del suelo en el pasto activo han respondido a corto plazo con una adaptación de su estructura ante la disponibilidad de sustrato, pero no han mostrado un cambio de sus funciones iniciales a largo plazo. Después de la aplicación de urea y de la roca fosfórica, se detectó un incremento significativo en la abundancia de los hongos, pero tampoco se observó una limitación de energía microbial ni de N o P. Sin embargo, la aplicación de urea ha aumentado la pérdida gaseosa de CO2‐C del suelo a corto plazo. Debido al cambio de uso de la tierra en la área de investigación, se ha detectado una alteración notable de la función del ecosistema, especialmente en el ciclo de C y N de suelo. Para un uso sostenible de la tierra en esta región, es crucial el prevenir la degradación de pastos y rehabilitar aquellos degradados. En el suelo de pastos activos es de gran importancia el mantener o aún mejor el aumentar la disponibilidad del sustrato, que es uno de los indicadores de la fertilidad del suelo. En este contexto, la materia orgánica se debe ser retenida a largo plazo para mantener la actividad y biomasa microbiana alta y por ende la productividad de pasto. Una moderada fertilización con urea y roca fosfórica puede ser un primer paso para proveer un continuo suministro de nutrientes por el crecimiento del pasto y para reforzar la sanidad pecuaria por medio de un forraje de mayor calidad. Sin embargo, el riesgo de emisiones adicionales de CO2‐C del suelo debido a una aplicación más alta de urea debe tenerse en cuenta. Se puede concluir que para un manejo sostenible del uso de la tierra, tanto el control de la invasión de Llashipa y como un suministro adecuado de nutrientes son necesarios. Adicionalmente se podría decir que es necesario profundizar el estudio de la reducción de las pérdidas de los nutrientes de suelo y de la eficiencia del uso de los nutrientes en las plantas, así como las asociaciones de pastos con leguminosas o el uso de cultivos de absorción selectiva de nutrientes, que serían estrategias importantes para el futuro.

El reg amb aigües residuals tractades s'ha convertit avui en dia en una necessitat, ja que permet preservar els recursos hídrics de més qualitat i constitueix una alternativa necessària per al manteniment de regadius tradicionals. En aquesta tesi s'avaluen els efectes del reg amb aigües residuals tractades d'origen domèstic sobre les característiques químiques i biològiques de diferents tipologies de sòls a l'illa de Mallorca, així com sobre el creixement dels cultius i la seva composició mineral mitjançant diferents estudis de camp i en cultius en contenidors. En general no s'han apreciat efectes negatius importants causats pel reg amb aquestes aigües excepte alguns valors puntualment més elevats de crom i plom que es relacionen amb aportacions d'aigües poc depurades realitzades en el passat. Segons els resultats obtinguts amb el reg amb aigües residuals tractades d'origen domèstic es contribueix a millorar la qualitat del sòl i s'aporten part dels nutrients que requereixen els cultius per al seu creixement. / El riego con aguas residuales tratadas se ha convertido hoy en día en una necesidad, ya que permite preservar los recursos hídricos de más calidad y constituye una alternativa necesaria para el mantenimiento de regadíos tradicionales. En esta tesis se evalúan los efectos del riego con aguas residuales tratadas de origen doméstico sobre las características químicas i biológicas de diferentes tipologías de suelos en la isla de Mallorca, así como sobre el crecimiento de los cultivos y su composición mineral mediante diferentes estudios de campo i en cultivos en contenedores. En general no se han apreciado efectos negativos importantes causados por el riego con estas aguas, excepto algunos valores puntualmente más elevados de cromo y plomo que se relaciona con aportaciones de aguas poco depuradas realizadas en el pasado. Según los resultados obtenidos con el riego con aguas residuales tratadas de origen doméstico se contribuye a mejorar la calidad del suelo y se aportan parte de los nutrientes que requieren los cultivos para su crecimiento. / Nowadays the irrigation with treated waste water has become a necessity, not only, because it allows preserving fresh water but it also constitutes an important alternative to the maintenance of traditional irrigating lands. Considering different chemical and biological characteristics of soil samples of Mallorca island (Spain), this thesis investigates the effect of irrigation with treated domestic waste water on soil properties. In addition, several studies were conducted in a series of pot experiments and land conditions to monitor the crops growth and evaluate their mineral compositions. In general, no negative effects caused by this type of irrigation have been observed, except of some high values of chromium and lead which were related to past irrigation realized with untreated effluents. According to our results, the irrigation with treated domestic wastewater contributes to improve soil quality and supplies part of the nutrient requirements of the crops.

No description available.

In the present thesis, implications of pasture establishment, fertilization and abandonment on soil C and nutrient dynamics were investigated for the mountain rainforest region of southern Ecuador. Over the past decades the natural forest of the study area has been threatened by conversion to cattle pastures. However, the soil fertility of these extensively grazed pastures (active pastures) declines continuously during pasture use. The invasion of bracken fern (Pteridium arachnoideum) leads to pasture abandonment when bracken becomes dominant. In order to reveal the mechanisms behind the deterioration of soil fertility, biotic and abiotic soil properties and their interaction were analyzed along a land‐use gradient (natural forest – active pasture – abandoned pasture). The ecosystem disturbance of the mountain rainforest through pasture use changed the microbial function and structure, and affected soil CO2‐C fluxes. Annually, 2 Mg soil CO2‐C ha‐1 were additionally emitted from the pasture land. This acceleration in soil respiration rates was related to accelerated rates of microbial C mineralization and fine‐root respiration. The high‐quality, N‐rich above‐ and belowground residues of the pasture grass (S. sphacelata, C4‐plant), especially the huge fine‐root biomass, provided a high C and N availability for soil microbes. Compared to the forest, increased soil pH and accelerated base saturation were further factors beneficial for soil microbial growth and metabolism of the upper mineral soil at active pastures. Three times higher amounts of microbial biomass C and a significant shift in the microbial community structure towards a higher relative abundance of Gram(‐)‐ bacteria and fungi were observed. Long‐term pasture use and the invasion of bracken (C3‐plant) diminished beneficial effects for microbes, causing a significant decrease in the C, net, and gross N mineralization rates as well as a two‐third reduction in the microbial biomass. A preferential substrate utilization of grass‐derived C4 by the soil microbes resulted in a rapid decline of the C4‐pool. As a consequence, the less available C3‐pool from bracken and former forest increased its dominance in the SOC‐pool, further decreasing pasture productivity and finally causing pasture abandonment. The lower quality and quantity of above‐ and belowground residues of the bracken (high lignin content, C/N) resulted in resource‐limited conditions that influenced the microbial function to greater extent than their structure. The microbial structure seemed to be sensitive mainly to soil pH along the land‐use gradient. Thus, a disconnection between microbial structure and function was identified. Fertilization experiments were conducted both in the lab and in the field to evaluate the impact of urea and/or rock phosphate amendment on SOM dynamics and on pasture productivity of active pastures. After combined fertilization the pasture yield was most efficiently increased by 2 Mg ha−1 a−1, indicating a NP‐limitation of grass growth. Furthermore, the fodder quality was improved by a higher content of P and Ca in the grass biomass. The microorganisms of the active pasture soil responded with an adaptation of their structure to the increased substrate availability in the short term, but did not change their initial functions in the long term. After urea/ rock phosphate addition a significant increase in the relative fungal abundance was detected, but neither a microbial limitation of energy nor of N or P was observed. However, urea addition accelerated gaseous losses of soil CO2‐C in the short term. In the study area, pronounced alterations in ecosystem functioning due to land‐use changes were detected, especially in soil C and N cycling rates. For a sustainable land‐use in this region it is crucial to prevent pasture degradation and to rehabilitate degraded pastures in order to protect the prevailing mountain rainforest ecosystem. It is of crucial importance for active pasture soils to maintain or even increase resource availability, being one indicator of soil fertility. In this context, the soil organic matter has to be retained in the long‐term to maintain high microbial activity and biomass, and thus pasture productivity. A moderate fertilization with urea and rock phosphate can be a first step to provide continuous nutrient supply for grass growth and to strengthen livestock health through increased fodder quality. However, the risk of further additional emissions of soil CO2‐C due to increased loads of urea fertilizer application has to be kept in mind. Overall, for the establishment of a sustainable land‐use management the control of bracken invasion and an adjusted nutrient management are needed. Further investigations on the reduction of soil nutrient losses and increased nutrient use efficiencies of plants, such as combined planting with legumes or the usage of cultivars with special nutrient acquisition strategies, should be in the focus of future work.:Contents Acknowledgement I Table of content III List of Tables V List of Figures VI Abbreviations VII Summary (English/German/Spanish) .................................................... 1 1 Introduction ................................................................................... 6 1.1 Impact of land‐use changes on C and nutrient dynamics ............... 6 1.1.1 Soil organic carbon and soil CO2 flux 7 1.1.2 The role of soil microbes 8 1.1.3 Plant‐microbe interactions 10 1.1.4 Impact of soil environment on soil microbes 11 1.2 Pasture establishment in the tropics .......................................... 13 1.3 Research area ....................................................................... .... 15 2 Objectives and research questions ......................... ................... 19 2.1 Land‐use change ........................................................................ 19 2.2 Pasture management ............................................................. ... 21 3 Methodology ................................................................................. 22 3.1 Study sites ............................................................................... 22 3.1.1 Land‐use gradient 22 3.1.2 Pasture Fertilization Experiment (FERPAST) 23 3.2 General analyses ....................................................................... 24 3.2.1 Laboratory experiments 25 3.2.2 In situ measurements 26 3.2.3 Statistics 27 4 Results ............................................................................................ 28 4.1 Soil C and nutrient dynamics along a land‐use gradient ............. 28 Potthast, K., Hamer, U., Makeschin, F., 2011. Land‐use change in a tropical mountain rainforest region of southern Ecuador affects soil microorganisms and nutrient cycling. Biogeochemistry, 1‐17. 4.2 Impact of pH and ongoing succession on microbial function and structure .......... 29 4.3 Response of soil microbes to bracken‐invasion ........................... 32 Potthast K., Hamer U., Makeschin F. 2010. Impact of litter quality on mineralization processes in managed and abandoned pasture soils in Southern Ecuador. Soil Biology and Biochemistry 42, 56‐64. 4.4 Response of soil microbes and pasture grass to fertilization ........33 Hamer, U., Potthast, K., Makeschin, F., 2009. Urea fertilisation affected soil organic matter dynamics and microbial community structure in pasture soils of Southern Ecuador. Applied Soil Ecology 43, 226‐233. Potthast, K., Hamer, U., Makeschin, F., 2012. In an Ecuadorian pasture soil the growth of Setaria sphacelata, but not of soil microorganisms, is co‐limited by N and P. Applied Soil Ecology 62, 103‐114. 5 Discussion .................................................................................... 34 5.1 Impact of land‐use changes ...................................................... 34 5.1.1 Soil CO2 fluxes 34 5.1.2 Microbial structure and function 34 5.2 Soil fertility loss of pastures ‐reasons and first prevention steps‐ . 37 5.2.1 Litter decay and SOM dynamics 37 5.2.2 Fertilization and SOM dynamics 39 5.3 Conclusions and Perspectives ...................................................... 42 References ..................................................................................... 46 Curriculum vitae......................................................................... 58 / In der vorliegenden Dissertation werden die Auswirkungen der Weideetablierung, ‐düngung sowie des Verlassens von Weiden auf Bodenkohlenstoff‐ und Nährstoffdynamik in einer tropischen Bergregenwaldregion Ecuadors zusammenfassend dargestellt und diskutiert. Der Naturwald des Untersuchungsgebietes ist seit Jahrzehnten durch Brandrodung und die Umwandlung in extensiv genutztes Weideland (aktive Weide) in seinem flächenhaften Bestand bedroht. Als Problem hat sich der Verlust an Fruchtbarkeit der Weideböden während ihrer Bewirtschaftung herausgestellt. Des Weiteren führt die Einwanderung des Tropischen Adlerfarns (Pteridium arachnoideum, C3‐Pflanze) zu einer Reduktion der oberirdischen Grasbiomasse. Nimmt diese Entwicklung überhand, werden die betroffenen Flächen von den Bauern nicht mehr aktiv genutzt, verlassen und neuer Regenwald gerodet. Um mehr über die Mechanismen der Verringerung der Bodenfruchtbarkeit zu erfahren, wurden biotische und abiotische Bodeneigenschaften und deren Interaktion entlang eines Landnutzungsgradienten (Naturwald – aktive Weide – verlassene Weide) untersucht. Die Zerstörung des Bergregenwaldökosystems und die Überführung der gerodeten Flächen zur Weidebewirtschaftung verändert die Funktion und Struktur der Bodenmikroorganismen und beeinflusst den CO2‐C Fluss aus dem Boden. Jährlich werden 2 t CO2‐C ha‐1 zusätzlich vom Weideland emittiert. Diese Erhöhung der Bodenatmungsraten kann mit erhöhten Raten der mikrobiellen C‐Mineralisierung und Feinwurzelatmung in Verbindung gebracht werden. Das Weidegras (S. sphacelata, C4‐Pflanze) liefert C‐ und N‐reiche ober und unterirdische organische Substanz (z.B. durch die Feinwurzelbiomasse) und trägt damit zu einer Erhöhung der C‐ und N‐Verfügbarkeit für die mikroorganismen bei. Darüber hinaus stellen ein höherer pH‐Wert und eine erhöhte Basensättigung im oberen Mineralboden der aktiven Weide günstige Bedingungen für mikrobielles Wachstum und Metabolismus dar. Als Konsequenz sind die Gehalte an mikrobiellem Biomassekohlenstoff um das Dreifache erhöht und die mikrobiellen Gemeinschaftsstrukturen signifikant in Richtung einer höheren relativen Abundanz der Gram(‐)‐Bakterien und Pilze verschoben. Eine längerfristige Weidebewirtschaftung ohne Kompensation von Nährstoffverlusten sowie die Einwanderung des Tropischen Adlerfarnes verschlechterte die Bedingungen für die Mikroorganismen, was zu einem signifikanten Rückgang des SOC, der Netto‐ und Brutto‐N‐Mineralisierungsraten sowie zu einer Halbierung der mikrobiellen Biomasse führt. Eine bevorzugte Substratnutzung von Graskohlenstoff (C4) durch die Mikroorganismen hat einen schnellen Abbau des C4‐Pools zur Folge. Somit dominiert nun der mikrobiell schlechter verfügbare C3‐Pool den Bodenkohlenstoffpool. Dies führt zu einem weiteren Rückgang der Weideproduktivität und schließlich zum Offenlassen der Weide. Die geringere Qualität und Quantität der vom Farn stammenden ober‐ und unterirdischen organischen Substanz (hoher Ligninanteil, weites C/N), führten zu einer Limitierung der Ressourcen für die Mikroorganismen, welche deren Funktionen in größerem Maße beeinflussen als deren Gemeinschaftsstruktur. Im Gegensatz dazu wird entlang des Landnutzungsgradienten die Struktur hauptsächlich durch den pH‐Wert beeinflusst. Daraus folgt, dass Struktur und Funktion der Bodenmikroorganismen voneinander entkoppelt auf Veränderungen reagieren können. Um den Einfluss von Harnstoff‐ und/ oder Rohphosphatdüngung aktiver Weiden auf die Dynamik der organischen Bodensubstanz und auf die Weideproduktivität zu untersuchen, wurden sowohl Labor‐ als auch Feldversuche durchgeführt. Im Feldexperiment wurde gezeigt, dass eine NP‐Limitierung der Grasbiomasseproduktion vorliegt und durch eine geringe NP‐Kombinationsdüngung die oberirdische Phytomasseproduktion um 2 t ha−1 a−1 gesteigert und die Futterqualität durch eine Erhöhung der P‐ und Ca‐ Gehalte verbessert werden kann. Die Mikroorganismen reagierten mit einer Anpassung ihrer Struktur an die kurzzeitig erhöhte Substratverfügbarkeit. Nach Gabe von Harnstoff und/ oder Rohphosphat wurde weder eine N‐ noch eine P‐Limitierung der Bodenmikroorganismen festgestellt, und die mikrobiellen Funktionen wurden langfristig nicht verändert. Dagegen bewirkte die Düngergabe einen erhöhten relativen Anteil der Pilzabundanz. Im Labor sowie im Feld kam es nach Harnstoffdüngung kurzzeitig zu verstärkten gasförmigen Verlusten des Bodenkohlenstoffs. Aufgrund der Landnutzungsänderungen im Untersuchungsgebiet veränderten sich die Ökosystemfunktionen stark, speziell die Boden‐C‐ und Boden‐N‐Umsatzraten. Für eine nachhaltige Landnutzung in der Region, d. h., für den Schutz der noch verbliebenen natürlichen Bergregenwaldflächen, ist es von entscheidender Bedeutung, dass die Weidedegradierung verhindert wird und degradierte Flächen wieder in Nutzung genommen werden. Als entscheidend für die Weideproduktivität hat sich in dieser Studie die Ressourcenverfügbarkeit für Bodenmikroorganismen herausgestellt. Daher ist es sehr wichtig, diese Ressourcenverfügbarkeit in Böden aktiv‐genutzter Weiden zu erhalten oder noch zu erhöhen, denn sie wirkt sich vor allem auf die organische Bodensubstanz und im Wechselspiel damit auf die mikrobielle Biomasse und Aktivität aus. Eine moderate Kombinationsdüngung aus Harnstoff und Rohphosphat ist ein erster Schritt in diese Richtung. Dabei sollte jedoch das Risiko zusätzlicher bodenbürtiger CO2‐C Emissionen in Folge höherer Düngergaben berücksichtigt werden. Für ein nachhaltiges Landnutzungsmanagement sind Maßnahmen gegen die Einwanderung des Adlerfarnes und ein angepasstes Nährstoffmanagement notwendig. Weitere Untersuchungen sollten auf eine Minimierung der Nährstoffverluste und eine erhöhte Nährstoffnutzungseffizienz der Pflanzen fokussiert werden. Weidemischkulturen aus Gräsern mit Leguminosen sowie der Einsatz von Kulturen mit speziellen Nährstoffaneignungsstrategien könnten dabei eine große Rolle spielen und sollten in der Region erprobt werden.:Contents Acknowledgement I Table of content III List of Tables V List of Figures VI Abbreviations VII Summary (English/German/Spanish) .................................................... 1 1 Introduction ................................................................................... 6 1.1 Impact of land‐use changes on C and nutrient dynamics ............... 6 1.1.1 Soil organic carbon and soil CO2 flux 7 1.1.2 The role of soil microbes 8 1.1.3 Plant‐microbe interactions 10 1.1.4 Impact of soil environment on soil microbes 11 1.2 Pasture establishment in the tropics .......................................... 13 1.3 Research area ....................................................................... .... 15 2 Objectives and research questions ......................... ................... 19 2.1 Land‐use change ........................................................................ 19 2.2 Pasture management ............................................................. ... 21 3 Methodology ................................................................................. 22 3.1 Study sites ............................................................................... 22 3.1.1 Land‐use gradient 22 3.1.2 Pasture Fertilization Experiment (FERPAST) 23 3.2 General analyses ....................................................................... 24 3.2.1 Laboratory experiments 25 3.2.2 In situ measurements 26 3.2.3 Statistics 27 4 Results ............................................................................................ 28 4.1 Soil C and nutrient dynamics along a land‐use gradient ............. 28 Potthast, K., Hamer, U., Makeschin, F., 2011. Land‐use change in a tropical mountain rainforest region of southern Ecuador affects soil microorganisms and nutrient cycling. Biogeochemistry, 1‐17. 4.2 Impact of pH and ongoing succession on microbial function and structure .......... 29 4.3 Response of soil microbes to bracken‐invasion ........................... 32 Potthast K., Hamer U., Makeschin F. 2010. Impact of litter quality on mineralization processes in managed and abandoned pasture soils in Southern Ecuador. Soil Biology and Biochemistry 42, 56‐64. 4.4 Response of soil microbes and pasture grass to fertilization ........33 Hamer, U., Potthast, K., Makeschin, F., 2009. Urea fertilisation affected soil organic matter dynamics and microbial community structure in pasture soils of Southern Ecuador. Applied Soil Ecology 43, 226‐233. Potthast, K., Hamer, U., Makeschin, F., 2012. In an Ecuadorian pasture soil the growth of Setaria sphacelata, but not of soil microorganisms, is co‐limited by N and P. Applied Soil Ecology 62, 103‐114. 5 Discussion .................................................................................... 34 5.1 Impact of land‐use changes ...................................................... 34 5.1.1 Soil CO2 fluxes 34 5.1.2 Microbial structure and function 34 5.2 Soil fertility loss of pastures ‐reasons and first prevention steps‐ . 37 5.2.1 Litter decay and SOM dynamics 37 5.2.2 Fertilization and SOM dynamics 39 5.3 Conclusions and Perspectives ...................................................... 42 References ..................................................................................... 46 Curriculum vitae......................................................................... 58 / La tesis presentada investiga el impacto del establecimiento de pasto, de su fertilización y de su manejo tradicional (abandono del pastizal) a la dinámica del carbono y de los nutrientes de suelo en la región de los bosques tropicales montañosos en el Sur de Ecuador. Durante las últimas décadas el bosque natural en el área de estudio ha estado amenazada por su conversión a pastizales. Sin embargo, la fertilidad del suelo en pastos de tipo extensivo (pastos activos) decrece frecuentemente durante el uso de los pastos. La invasión de Llashipa (Pteridium arachnoideum) conduce al abandono de los pastos cuando la ésta se vuelve dominante. Con la finalidad de revelar los mecanismos detrás de esta disminución de la fertilidad de suelo, se analizaron las propiedades bióticas y abióticas del suelo y sus interacciones, a lo largo de una gradiente del uso de la tierra (bosque natural —pasto activo — pastos abandonados). La perturbación del ecosistema de bosque tropical montañoso por su cambio de uso, mediante el establecimiento de pastizales, ha alterado la función y la estructura de los microorganismos y ha afectado el flujo de CO2‐C del suelo. Cada año 2 Mg CO2‐C ha‐1 fueron emitidas adicionalmente por el establecimiento de pastos. Esta aceleración en la tasa de respiración del suelo está relacionada con el aumento de las tasas de mineralización microbiana de carbono y de la respiración de las raíces. La alta calidad y abundancia de N de los residuos orgánicos del suelo con pasto Mequeron (S. sphacelata, C4‐planta), especialmente debido a la gran biomasa de las raíces finas, ofrecen una disponibilidad alta de C y N para los microorganismos. En comparación con el bosque natural, el aumento del pH y la saturación bases acelerada fueron condiciones más favorables para el crecimiento microbiano y para el metabolismo microbiano en el parte superior del suelo mineral en pastos activos. La cantidad de C de la biomasa de los microorganismos fue tres veces mayor que la del bosque y se ha observado un cambio significativo de la estructura de la comunidad microbiana, en donde la abundancia relativa de los hongos y de las bacterias Gram(‐) ha aumentado. El uso de pasto a largo plazo y la invasión de Llashipa (C3‐planta) han reducido los efectos benéficos para los microorganismos, que resultaron en una reducción significativa de las tasas de la mineralización de C y N, y en una reducción en dos tercios de la biomasa microbiana. El uso preferencial de los microorganismos por sustrato de pasto C4 han resultado en una rápida disminución de la reserva de C4. Como consecuencia, la menor disponibilidad de la reserva de C3 de las plantas de Llashipa y de la cobertura anterior de bosque ha incrementado su dominancia en la reserva de materia orgánica del suelo. Eso resulta, en una mayor disminución de la productividad de los pastos, conduciendo finalmente al abandono de los campos de pastos. La menor calidad y cantidad de los residuos acumulados sobre y bajo el suelo provenientes de la Llashipa han dado como resultado un sustrato de limitadas condiciones que están afectando más a las funciones microbiales antes que a su estructura. La estructura microbiana parece ser más sensible al pH del suelo a largo de la gradiente del uso de la tierra; de manera que se ha identificado una desconexión entre la estructura y función microbial. Experimentos de fertilización en laboratorio y en campo han sido realizados para evaluar el impacto de la aplicación de enmiendas (urea y/o roca fosfórica) a la dinámica de la materia orgánica y a la productividad de los pastos activos. El resultado del experimento de campo ha demostrado que la fertilización combinada es más efectiva, mostrando un aumento en la producción de biomasa de 2 Mg ha−1 a−1, lo que indica una limitación de N y P para el crecimiento del pasto. Además, la calidad de forraje se mostró incrementada ya que el contenido de P y de Ca han aumentado significativamente. Los microorganismos del suelo en el pasto activo han respondido a corto plazo con una adaptación de su estructura ante la disponibilidad de sustrato, pero no han mostrado un cambio de sus funciones iniciales a largo plazo. Después de la aplicación de urea y de la roca fosfórica, se detectó un incremento significativo en la abundancia de los hongos, pero tampoco se observó una limitación de energía microbial ni de N o P. Sin embargo, la aplicación de urea ha aumentado la pérdida gaseosa de CO2‐C del suelo a corto plazo. Debido al cambio de uso de la tierra en la área de investigación, se ha detectado una alteración notable de la función del ecosistema, especialmente en el ciclo de C y N de suelo. Para un uso sostenible de la tierra en esta región, es crucial el prevenir la degradación de pastos y rehabilitar aquellos degradados. En el suelo de pastos activos es de gran importancia el mantener o aún mejor el aumentar la disponibilidad del sustrato, que es uno de los indicadores de la fertilidad del suelo. En este contexto, la materia orgánica se debe ser retenida a largo plazo para mantener la actividad y biomasa microbiana alta y por ende la productividad de pasto. Una moderada fertilización con urea y roca fosfórica puede ser un primer paso para proveer un continuo suministro de nutrientes por el crecimiento del pasto y para reforzar la sanidad pecuaria por medio de un forraje de mayor calidad. Sin embargo, el riesgo de emisiones adicionales de CO2‐C del suelo debido a una aplicación más alta de urea debe tenerse en cuenta. Se puede concluir que para un manejo sostenible del uso de la tierra, tanto el control de la invasión de Llashipa y como un suministro adecuado de nutrientes son necesarios. Adicionalmente se podría decir que es necesario profundizar el estudio de la reducción de las pérdidas de los nutrientes de suelo y de la eficiencia del uso de los nutrientes en las plantas, así como las asociaciones de pastos con leguminosas o el uso de cultivos de absorción selectiva de nutrientes, que serían estrategias importantes para el futuro.:Contents Acknowledgement I Table of content III List of Tables V List of Figures VI Abbreviations VII Summary (English/German/Spanish) .................................................... 1 1 Introduction ................................................................................... 6 1.1 Impact of land‐use changes on C and nutrient dynamics ............... 6 1.1.1 Soil organic carbon and soil CO2 flux 7 1.1.2 The role of soil microbes 8 1.1.3 Plant‐microbe interactions 10 1.1.4 Impact of soil environment on soil microbes 11 1.2 Pasture establishment in the tropics .......................................... 13 1.3 Research area ....................................................................... .... 15 2 Objectives and research questions ......................... ................... 19 2.1 Land‐use change ........................................................................ 19 2.2 Pasture management ............................................................. ... 21 3 Methodology ................................................................................. 22 3.1 Study sites ............................................................................... 22 3.1.1 Land‐use gradient 22 3.1.2 Pasture Fertilization Experiment (FERPAST) 23 3.2 General analyses ....................................................................... 24 3.2.1 Laboratory experiments 25 3.2.2 In situ measurements 26 3.2.3 Statistics 27 4 Results ............................................................................................ 28 4.1 Soil C and nutrient dynamics along a land‐use gradient ............. 28 Potthast, K., Hamer, U., Makeschin, F., 2011. Land‐use change in a tropical mountain rainforest region of southern Ecuador affects soil microorganisms and nutrient cycling. Biogeochemistry, 1‐17. 4.2 Impact of pH and ongoing succession on microbial function and structure .......... 29 4.3 Response of soil microbes to bracken‐invasion ........................... 32 Potthast K., Hamer U., Makeschin F. 2010. Impact of litter quality on mineralization processes in managed and abandoned pasture soils in Southern Ecuador. Soil Biology and Biochemistry 42, 56‐64. 4.4 Response of soil microbes and pasture grass to fertilization ........33 Hamer, U., Potthast, K., Makeschin, F., 2009. Urea fertilisation affected soil organic matter dynamics and microbial community structure in pasture soils of Southern Ecuador. Applied Soil Ecology 43, 226‐233. Potthast, K., Hamer, U., Makeschin, F., 2012. In an Ecuadorian pasture soil the growth of Setaria sphacelata, but not of soil microorganisms, is co‐limited by N and P. Applied Soil Ecology 62, 103‐114. 5 Discussion .................................................................................... 34 5.1 Impact of land‐use changes ...................................................... 34 5.1.1 Soil CO2 fluxes 34 5.1.2 Microbial structure and function 34 5.2 Soil fertility loss of pastures ‐reasons and first prevention steps‐ . 37 5.2.1 Litter decay and SOM dynamics 37 5.2.2 Fertilization and SOM dynamics 39 5.3 Conclusions and Perspectives ...................................................... 42 References ..................................................................................... 46 Curriculum vitae......................................................................... 58

No description available.