Existe uma necessidade urgente em monitorar as respostas da biodiversidade e dos processos ecológicos a distúrbios e mudanças no uso da terra. Diversos estudos tem indicado que o uso da abordagem funcional da biodiversidade, baseada em atributos funcionais, facilita a compreensão sobre a organização dos organismos nas comunidades, da funcionalidade dos ecossistemas, e desta forma, auxilia na identificação das suas relações com fatores ambientais. No primeiro capítulo desta tese eu apresento o arcabouço teórico da ecologia funcional aplicada ao estudo dos invertebrados terrestres, e reviso o que são atributos funcionais, como usá-los na descrição e monitoramento das comunidades e o porquê, ressaltando a ligação dos invertebrados com processos ecológicos. Nos próximos capítulos eu apresento estudos experimentais avaliando as respostas funcionais de dois grupos de invertebrados - aranhas (Araneae) e tripes (Thysanoptera) - e de processos ecológicos influenciados por invertebrados (detritivoria e decomposição de serapilheira) ao distúrbio por fogo nos Campos Sulinos. As queimadas representam uma estratégia de manejo frequente nas pastagens naturais do RS, e carecem em estudos avaliando seus efeitos no ambiente, biodiversidade e processos. A investigação foi realizada com base em um experimento de queima controlada na Estação Agronômica da UFRGS, em Eldorado do Sul, RS. O design foi em blocos casualizados, com 14 parcelas experimentais de 10 x 10 m pareadas; sendo uma parcela de cada bloco queimada no final da primavera de 2009, e a outra, considerada como controle. Informações sobre invertebrados, processos ecológicos e propriedades abióticas do hábitat foram obtidas em todas parcelas antes do fogo (para a caracterização inicial), e 1 mês, 6-7 meses e 12 meses após o fogo. Para o estudo de caso com aranhas, eu classifiquei as comunidades em famílias, atributos de estratégias de caça e medi todos os indivíduos (1755) em atributos funcionais morfológicos, sendo incorporada toda a variabilidade intra e interespecífica, e fenológica das comunidades. Por outro lado, no estudo de caso com tripes, descrevi atributos funcionais (hábitos alimentares, requerimentos de hábitat e atributos morfológicos) por espécie de tripes (48 spp.), assumindo que a variação nos atributos funcionais é sempre maior entre espécies do que dentro da mesma espécie. Nos dois estudos de caso, eu encontrei padrões indicativos de filtragem ambiental, ou seja, o fogo e/ou as mudanças no hábitat induzidas pelo fogo, parecem ter atuado como um filtro, selecionando organismos com determinado conjunto de atributos em detrimento de outros. Esses padrões foram dependentes do período após a queima considerado, por exemplo: um mês após o fogo aranhas construtoras de teias irregulares e tripes fungívoros foram prejudicados, enquanto que aranhas caçadoras da vegetação, com grandes quelíceras, tripes fitófagos e associados com gramíneas aumentaram suas proporções. Para aranhas ainda verifiquei convergência de atributos ao gradiente de biomassa induzido pelo fogo (filtragem ambiental), e divergência de atributos ao gradiente de heterogeneidade da vegetação, indicativo de limitação de similaridade (i.e. aumento da coexistência de organismos funcionalmente diferentes e diminuição de competição). Finalmente com relação aos processos ecológicos, encontrei correlações interessantes acerca de seus agentes modeladores, e.g. entre a atividade de detritivoria com a decomposição de serapilheira, e desta com a equidade da vegetação em campo não queimado. Também mostro que os processos são sensíveis, mas resilientes, ao distúrbio por fogo, seguindo a recuperação da estrutura de hábitat. Adicionalmente, eu incorporei à tese um capítulo sobre uma técnica para avaliar o processo de detritivoria, denominado bait-lamina test, o qual avalia diretamente as taxas de alimentação de invertebrados detritívoros do solo. Neste estudo pioneiro nos campos do RS, esclareço alguns aspectos metodológicos que possam constituir uma base para futuras pesquisas. Contudo, com esta tese espero estar contribuindo com o conhecimento sobre as respostas das comunidades de invertebrados e dos processos ecológicos ao distúrbio por fogo nos Campos Sulinos. Em geral, posso concluir que a abordagem funcional trouxe muitos benefícios ao monitoramento da biodiversidade, e que há elevada resiliência das assembléias de aranhas e tripes, e dos processos de detritivoria e decomposição às queimadas de pequena escala nos campos. / There is a huge need of monitoring the responses of biodiversity and ecological processes to disturbances and land use changes. Several studies have indicated that the functional approach of biodiversity, based on functional traits, facilitates the understanding of community assembly and ecosystem functionality, and thus assists on the identification of their relationships with environmental factors. In the first chapter of this Thesis I present the functional ecology theory applied to studies on terrestrial invertebrates, and I review what functional traits are, how to use them in community description and monitoring, and why, highlighting the connections between invertebrates and ecological processes. In the following chapters I present experimental studies evaluating the functional responses of two invertebrate groups- spiders (Araneae) and thrips (Thysanoptera) – and ecological processes influenced by invertebrates (detritivory and litter decay) to fire disturbance in Campos grasslands. Burning represents a common strategy for pasture management in Rio Grande do Sul State, and there is a lack of studies regarding their effects on the environment, biodiversity and processes. Our investigation was performed based in a burning experiment at Estação Agronômica of UFRGS, Eldorado do Sul, RS. The design was blocked, with 14 experimental paired plots of 10 x 10 m. One plot from each block was burned at the end of spring 2009, and the other is considered a control plot. Information concerning invertebrates, ecological processes and abiotic habitat proprieties were obtained from all plots before fire (initial characterization) and 1 month, 6-7 months and 12 months after fire. For the spider study case, I classified the organisms in families, feeding strategy traits, and measured all spider individuals (1755) thus incorporating all intra and interspecific variability of the communities. On the other hand, in the thrips study case I described functional traits (feeding habits, habitat requirements, and morphological traits) per species (48 spp.), assuming that the variation on functional traits should be higher between species than within species. In both cases, I found patterns indicating environmental filtering, which means that fire and/or the fire-induced habitat changes acted as a filter, sorting organisms with a determined group of traits instead of others. These patterns were dependent on the period after fire considered. For example, one month after fire irregular web spider builders and fungivorous thrips were more uncommon than expected, while vegetation hunter spiders, with large chelicerae, and leaf feeder thrips and thrips associated to grasses increased their proportions. For spiders we also verified a trait-convergence pattern along the plant biomass gradient induced by fire (environmental filtering), and trait-divergence pattern along the vegetation heterogeneity gradient indicating limiting similarity (i.e. increase in coexistence of functionally different organisms, and reduction of competition). Finally, regarding ecological processes, I found interesting correlations on their drivers, e.g. between detritivory and litter decay, and between these with plant evenness in unburned grasslands. Also, I show that ecological processes are sensitive but resilient to fire, following habitat structure recovery. Additionally, I incorporate to the Thesis a methodology chapter about the bait-lamina test, which evaluates the feeding rates of soil detritivore invertebrates directly. In this pioneer study, I clarify some methodological aspects of measuring invertebrate detritivory that could help future research. Nevertheless, with this Thesis I hope to contribute to the understanding of invertebrate community and ecological processes responses to fire disturbance in South Brazilian grasslands. Overall, I can conclude that a functional approach brings many benefits to biodiversity monitoring, and also that spiders and thrips communities, and detritivory and decomposition processes are very resilient to the change brought by small scale grassland burning.

Existe uma necessidade urgente em monitorar as respostas da biodiversidade e dos processos ecológicos a distúrbios e mudanças no uso da terra. Diversos estudos tem indicado que o uso da abordagem funcional da biodiversidade, baseada em atributos funcionais, facilita a compreensão sobre a organização dos organismos nas comunidades, da funcionalidade dos ecossistemas, e desta forma, auxilia na identificação das suas relações com fatores ambientais. No primeiro capítulo desta tese eu apresento o arcabouço teórico da ecologia funcional aplicada ao estudo dos invertebrados terrestres, e reviso o que são atributos funcionais, como usá-los na descrição e monitoramento das comunidades e o porquê, ressaltando a ligação dos invertebrados com processos ecológicos. Nos próximos capítulos eu apresento estudos experimentais avaliando as respostas funcionais de dois grupos de invertebrados - aranhas (Araneae) e tripes (Thysanoptera) - e de processos ecológicos influenciados por invertebrados (detritivoria e decomposição de serapilheira) ao distúrbio por fogo nos Campos Sulinos. As queimadas representam uma estratégia de manejo frequente nas pastagens naturais do RS, e carecem em estudos avaliando seus efeitos no ambiente, biodiversidade e processos. A investigação foi realizada com base em um experimento de queima controlada na Estação Agronômica da UFRGS, em Eldorado do Sul, RS. O design foi em blocos casualizados, com 14 parcelas experimentais de 10 x 10 m pareadas; sendo uma parcela de cada bloco queimada no final da primavera de 2009, e a outra, considerada como controle. Informações sobre invertebrados, processos ecológicos e propriedades abióticas do hábitat foram obtidas em todas parcelas antes do fogo (para a caracterização inicial), e 1 mês, 6-7 meses e 12 meses após o fogo. Para o estudo de caso com aranhas, eu classifiquei as comunidades em famílias, atributos de estratégias de caça e medi todos os indivíduos (1755) em atributos funcionais morfológicos, sendo incorporada toda a variabilidade intra e interespecífica, e fenológica das comunidades. Por outro lado, no estudo de caso com tripes, descrevi atributos funcionais (hábitos alimentares, requerimentos de hábitat e atributos morfológicos) por espécie de tripes (48 spp.), assumindo que a variação nos atributos funcionais é sempre maior entre espécies do que dentro da mesma espécie. Nos dois estudos de caso, eu encontrei padrões indicativos de filtragem ambiental, ou seja, o fogo e/ou as mudanças no hábitat induzidas pelo fogo, parecem ter atuado como um filtro, selecionando organismos com determinado conjunto de atributos em detrimento de outros. Esses padrões foram dependentes do período após a queima considerado, por exemplo: um mês após o fogo aranhas construtoras de teias irregulares e tripes fungívoros foram prejudicados, enquanto que aranhas caçadoras da vegetação, com grandes quelíceras, tripes fitófagos e associados com gramíneas aumentaram suas proporções. Para aranhas ainda verifiquei convergência de atributos ao gradiente de biomassa induzido pelo fogo (filtragem ambiental), e divergência de atributos ao gradiente de heterogeneidade da vegetação, indicativo de limitação de similaridade (i.e. aumento da coexistência de organismos funcionalmente diferentes e diminuição de competição). Finalmente com relação aos processos ecológicos, encontrei correlações interessantes acerca de seus agentes modeladores, e.g. entre a atividade de detritivoria com a decomposição de serapilheira, e desta com a equidade da vegetação em campo não queimado. Também mostro que os processos são sensíveis, mas resilientes, ao distúrbio por fogo, seguindo a recuperação da estrutura de hábitat. Adicionalmente, eu incorporei à tese um capítulo sobre uma técnica para avaliar o processo de detritivoria, denominado bait-lamina test, o qual avalia diretamente as taxas de alimentação de invertebrados detritívoros do solo. Neste estudo pioneiro nos campos do RS, esclareço alguns aspectos metodológicos que possam constituir uma base para futuras pesquisas. Contudo, com esta tese espero estar contribuindo com o conhecimento sobre as respostas das comunidades de invertebrados e dos processos ecológicos ao distúrbio por fogo nos Campos Sulinos. Em geral, posso concluir que a abordagem funcional trouxe muitos benefícios ao monitoramento da biodiversidade, e que há elevada resiliência das assembléias de aranhas e tripes, e dos processos de detritivoria e decomposição às queimadas de pequena escala nos campos. / There is a huge need of monitoring the responses of biodiversity and ecological processes to disturbances and land use changes. Several studies have indicated that the functional approach of biodiversity, based on functional traits, facilitates the understanding of community assembly and ecosystem functionality, and thus assists on the identification of their relationships with environmental factors. In the first chapter of this Thesis I present the functional ecology theory applied to studies on terrestrial invertebrates, and I review what functional traits are, how to use them in community description and monitoring, and why, highlighting the connections between invertebrates and ecological processes. In the following chapters I present experimental studies evaluating the functional responses of two invertebrate groups- spiders (Araneae) and thrips (Thysanoptera) – and ecological processes influenced by invertebrates (detritivory and litter decay) to fire disturbance in Campos grasslands. Burning represents a common strategy for pasture management in Rio Grande do Sul State, and there is a lack of studies regarding their effects on the environment, biodiversity and processes. Our investigation was performed based in a burning experiment at Estação Agronômica of UFRGS, Eldorado do Sul, RS. The design was blocked, with 14 experimental paired plots of 10 x 10 m. One plot from each block was burned at the end of spring 2009, and the other is considered a control plot. Information concerning invertebrates, ecological processes and abiotic habitat proprieties were obtained from all plots before fire (initial characterization) and 1 month, 6-7 months and 12 months after fire. For the spider study case, I classified the organisms in families, feeding strategy traits, and measured all spider individuals (1755) thus incorporating all intra and interspecific variability of the communities. On the other hand, in the thrips study case I described functional traits (feeding habits, habitat requirements, and morphological traits) per species (48 spp.), assuming that the variation on functional traits should be higher between species than within species. In both cases, I found patterns indicating environmental filtering, which means that fire and/or the fire-induced habitat changes acted as a filter, sorting organisms with a determined group of traits instead of others. These patterns were dependent on the period after fire considered. For example, one month after fire irregular web spider builders and fungivorous thrips were more uncommon than expected, while vegetation hunter spiders, with large chelicerae, and leaf feeder thrips and thrips associated to grasses increased their proportions. For spiders we also verified a trait-convergence pattern along the plant biomass gradient induced by fire (environmental filtering), and trait-divergence pattern along the vegetation heterogeneity gradient indicating limiting similarity (i.e. increase in coexistence of functionally different organisms, and reduction of competition). Finally, regarding ecological processes, I found interesting correlations on their drivers, e.g. between detritivory and litter decay, and between these with plant evenness in unburned grasslands. Also, I show that ecological processes are sensitive but resilient to fire, following habitat structure recovery. Additionally, I incorporate to the Thesis a methodology chapter about the bait-lamina test, which evaluates the feeding rates of soil detritivore invertebrates directly. In this pioneer study, I clarify some methodological aspects of measuring invertebrate detritivory that could help future research. Nevertheless, with this Thesis I hope to contribute to the understanding of invertebrate community and ecological processes responses to fire disturbance in South Brazilian grasslands. Overall, I can conclude that a functional approach brings many benefits to biodiversity monitoring, and also that spiders and thrips communities, and detritivory and decomposition processes are very resilient to the change brought by small scale grassland burning.

Mon travail de thèse s'est attaché à étudier les effets de la diversité des litières et de la macrofaune du sol sur les communautés microbienne, sous contrainte hydrique. Dans une première partie, le suivi des communautés microbiennes associées aux feuilles de la litière (feuilles mortes) et de la phyllosphère (feuilles vivantes), pendant un an en conditions naturelles, a montré des différences marquées selon l'état physiologique de la feuille, l'importance de l'espèce végétale hôte sur les communautés microbiennes ainsi que l'évolution des communautés au cours de l'année. Une deuxième partie présente les résultats d'une expérience de décomposition en microcosmes selon deux modalités d'humidité, un gradient de dissimilarité fonctionnelle des espèces de litière, et la présence/absence d'une macrofaune détritivore. Nos résultats confortent l'importance de l'espèce végétale sur les communautés microbiennes et montrent que la présence de détritivores favorise la diversité microbienne. Enfin, une dernière partie évalue l'impact d'une diminution des précipitations et de la diversité des litières sur les communautés microbiennes lors d'une expérience de décomposition d'un an in situ, à l'aide de dispositifs d'exclusion de pluie. La composition des mélanges de litières a une influence plus marquée sur les communautés microbiennes que la baisse des précipitations. En conclusion, les résultats de mes travaux ont tendance à minorer l'effet d'une diminution des précipitations sur les communautés microbiennes, mais soulignent la sensibilité des interactions entre communauté végétale, macrofaune et microorganismes face au changement climatique. / My PhD work focused on studying the effects of litter diversity and soil macrofauna on microbial communities under water stress. In the first part, the monitoring of microbial communities associated with leaf litter (dead leaves) and phyllosphere (living leaves) for one year under natural conditions, showed marked differences depending on the physiological state of leaves, the importance of the host plant species on microbial communities and the changes of communities during the year. A second part presents the results of a microcosms decomposition experience under two humidity conditions, a functional dissimilarity gradient of litter species and the presence / absence of a detritivorous macrofauna. Our results reinforce the importance of the plant species on microbial communities and show that the presence of scavengers encourages microbial diversity. A final section assesses the impact of a decrease in precipitation and litter diversity on microbial communities in an in situ decomposition experiment during one year, using rain excluder devices . The composition of litter mixtures has a stronger influence on the microbial communities than lower rainfall. In conclusion, the results of my work tend to underestimate the effect of a decrease in precipitation on microbial communities, but emphasize the sensitivity of the interactions between plant community, macro- and micro-organisms to climate change.

Litter decomposition is a key process for carbon and nutrient cycling in terrestrial ecosystems and is mainly controlled by environmental conditions, substrate quantity and quality as well as microbial community abundance and composition. In particular, the effects of climate and atmospheric nitrogen (N) deposition on litter decomposition and its temporal dynamics are of significant importance, since their effects might change over the course of the decomposition process. Within the TeaComposition initiative, we incubated Green and Rooibos teas at 524 sites across nine biomes. We assessed how macroclimate and atmospheric inorganic N deposition under current and predicted scenarios (RCP 2.6, RCP 8.5) might affect litter mass loss measured after 3 and 12 months. Our study shows that the early to mid-term mass loss at the global scale was affected predominantly by litter quality (explaining 73% and 62% of the total variance after 3 and 12 months, respectively) followed by climate and N deposition. The effects of climate were not litter-specific and became increasingly significant as decomposition progressed, with MAP explaining 2% and MAT 4% of the variation after 12 months of incubation. The effect of N deposition was litter-specific, and significant only for 12-month decomposition of Rooibos tea at the global scale. However, in the temperate biome where atmospheric N deposition rates are relatively high, the 12- month mass loss of Green and Rooibos teas decreased significantly with increasing N deposition, explaining 9.5% and 1.1% of the variance, respectively. The expected changes in macroclimate and N deposition at the global scale by the end of this century are estimated to increase the 12-month mass loss of easily decomposable litter by 1.1– 3.5% and of the more stable substrates by 3.8–10.6%, relative to current mass loss. In contrast, expected changes in atmospheric N deposition will decrease the mid-term mass loss of high-quality litter by 1.4–2.2% and that of low-quality litter by 0.9–1.5% in the temperate biome. Our results suggest that projected increases in N deposition may have the capacity to dampen the climate-driven increases in litter decomposition depending on the biome and decomposition stage of substrate.

No description available.

Boreal forests are often strongly nitrogen (N) limited. However, human activities are leading to increased N inputs into these ecosystems, through atmospheric N deposition and forest fertilization. N input into boreal forests can promote net primary productivity, increase herbivore and pathogen damage, and shift plant species composition and community structure. Genetic diversity has been suggested as a key mechanism to promote a plant species’ stability within communities in response to environmental change. Within any plant population, specific traits (e.g. growth and defense traits) can vary substantially among individuals, and a greater variation in traits may increase chances for the persistence of at least some individuals of a population, when environmental conditions change. One aspect of plant chemistry that can greatly vary among different genotypes (GTs) are condensed tannin (CTs). These secondary metabolites have been suggested to affect plant performance in many ways, e.g. through influencing plant growth, the interactions of plants with herbivores and pathogens, and through affecting litter decomposition, and hence the return of nutrients to plants. To investigate how genotypic variation in foliar CT production may mediate the effects that anthropogenic N enrichment can have on plant performance and litter decomposition, I performed a series of experiments. For these experiments, aspen (Populus tremula) GTs with contrasting abilities to produce foliar CTs (i.e. low- vs. high-tannin producers) were grown under 3 N conditions, representing ambient N (+0 kg ha-1), upper level atmospheric N deposition (+15 kg ha-1), and forest fertilization rates (+150 kg ha-1). This general experimental set-up was once established in a field-like environment, from which natural enemies were excluded, and once in a field, in which enemies were present. In my first two studies, I investigated tissue chemistry and plant performance in both environments. I observed that foliar CT levels decreased in response to N in the enemy‑free environment (study I), but increased with added N when enemies were present (study II). These opposing responses to N may be explained by differences in soil N availability in the two environments, or by induction of CTs after enemy attack. Enemy damage generally increased in response to N, and was higher in low-tannin than in high-tannin plants across all N levels. Plant growth of high‑tannin plants was restricted under ambient and low N conditions, probably due to a trade-off between growth and defense. This growth constraint for high‑tannin plants was weakened, when high amounts of N were added (study I and II), and when enemy levels were sufficiently high, so that benefits gained through defense could outweigh the costs of defense production (study II). Despite those general responses of low- and high‑tannin producers to added N, I also observed a number of individual responses of GTs to N addition, which in some case were not connected to the intrinsic ability of the GTs to produce foliar CTs. In study III, gene expression levels in young leaves and phenolic pools of the plants that were grown in the enemy‑free environment were studied. This study revealed that gene control over the regulation of the phenylpropanoid pathway (PPP) was distributed across the entire pathway. Moreover, PPP gene expression was higher in high-tannin GTs than in low‑tannin GTs, particularly under ambient N. At the low N level, gene expressions declined for both low- and high-tannin producers, whereas at the high N level expression at the beginning and the end of the PPP was upregulated and difference between tannin groups disappeared. Furthermore, this study showed that phenolic pools were frequently uncorrelated, and that phenolic pools were only to some extent related to tannin production and gene expression. In study IV, I investigated the decomposability of litter from the field plants. I found that N enrichment generally decreased mass loss, but there was substantial genetic variation in decomposition rates, and GTs were differentially responsive to added N. Study IV further showed that CTs only had a weak effect on decomposition, and other traits, such as specific leaf area and the lignin:N ratio, could better explain genotypic difference in mass loss. Furthermore, N addition caused a shift in which traits most strongly influenced decomposition rates. Collectively, the result of these studies highlight the importance of genetic diversity to promote the stability of species in environments that experience anthropogenic change. / Boreala skogar är ofta mycket kväve (N) begränsade. Men mänskliga aktiviteter leder till ökad N tillförsel i dessa ekosystem, både genom depostition av N från atmosfären och skogsgödsling. N-tillförsel i boreala skogar kan främja netto primärproduktionen men även leda till ökade skador från naturliga fiender (herbivorer och patogener) samt skiftningar i växtartsammansättning. Genetisk mångfald har föreslagits som en viktig mekanism för att främja en växtarts stabilitet inom samhällen som upplever miljöförändringar. Inom varje växtpopulation kan specifika egenskaper (t.ex. tillväxt och försvar) varierar kraftigt mellan individer och en större variation i egenskaper kan öka chanserna för att åtminstone några individer från en population överlever ifall miljöförhållandena förändras. En aspekt av växtkemi som i hög grad kan variera mellan olika genotyper (GT) är bladens kondenserade tanniner (KT). Dessa sekundära metaboliter har föreslagits påverka växtens prestationsförmåga på många sätt, t.ex. genom att påverka tillväxt, interaktioner mellan växter och herbivorer eller patogener och genom att påverka förna nedbrytning, och följaktligen återbördandet av näringsämnen till kretsloppet. För att undersöka hur genotypiska variation i KT produktion kan påverka de effekter som antopogent N kan ha på växtens prestationsförmåga och förna nedbrytning, utförde jag en serie experiment. Jag studerade olika asp (Populus tremula) GT med olika förmåga att producera KT (låg- och hög-tannin producenter). Växterna odlades i tre olika N förhållanden, som representerade ambient N nivå (+0 kg ha-1), atmosfärisk N deposition = låg nivå (+15 kg ha-1), och skogsgödsling = hög nivå (150 kg ha‑1). Dessa GT etablerades i en fält-liknande miljö där naturliga fiender uteslutits och i ett fält där naturliga fiender var närvarande. I mina första två studierna undersökte jag vävnadskemi och växternas prestationsförmåga i de båda miljöerna. Jag observerade att KT nivåerna sjönk till följd av N‑tillsats i den fiende-fria miljön (studie I), men ökade med N-tillsats ifall fiender var närvarande (studie II). Dessa motsatta reaktioner på N-tillsats kan förklaras av skillnader i N-tillgång mellan de två odlingsplatserna eller genom ökad KT produktion som respons på angrepp. Skador orsakade av herbivorer och patogener ökade generellt till följd av N‑tillsats och var högre i låg-tannin än i hög‑tannin producerande GT oavsett N‑förhållande. Tillväxten hos växter från hög‑tannin GT begränsades i ambient- och låg N-tillsats förhållanden, troligen på grund av att avvägning mellan tillväxt och försvar förskjutits emot försvar. Den begränsade tillväxten i hög-tannin växter minskade om stora mängder N tillsattes (studie I och II) och om antalet fiender var tillräckligt högt så att nyttan av försvaret kunde uppväga kostnaderna för försvarsproduktionen (studie II). Trots dessa generella respons hos låg- och hög-tannin GT till följd av N‑tillsats observerade jag även ett antal individuella respons hos GT som i vissa fall var orelaterade till växters förmåga att producera KT. I studie III undersöktes genuttrycksnivåer och fenolinnehåll i blad från växter som odladats i en miljö där naturliga fiender exkluderats. Denna studie visade att fenylpropanoidsyntesvägen (FPV) regleras genom kontroll av många av de undersökta FPV-generna. Dessutom var FPV genuttryck högre i hög-tannin GT än i låg-tannin GT, särskilt vid ambient N. Vid låg N-tillsats minskade genuttrycket av FPV-gener i både låg- och hög-tannin producenter, medan hög N-tillgång ledde till att gener i början och slutet av FPV uppreglerades och till att skillnaderna mellan tannin grupperna försvann. Dessutom visade studien att de separata fenol-poolerna ofta var okorrelerade med varandra och att fenol-poolerna bara till viss del var korrelerade med KT produktion och FPV-genutryck. I studie IV undersökte jag nedbrytningshastigheten för förnan från fältodlade aspar. Jag upptäckte att N-tillsats generellt minskade viktförlusten men att det fanns en betydande genetisk variation mellan GT och att dessa även var olika mottagliga för tillsatt N. Studie IV visade vidare att KT endast hade en svag effekt på nedbrytning och att andra egenskaper såsom specifik bladyta och lignin:N ratio kunde bättre förklara den genotypiska skillnaden i viktförlust. Dessutom orsakade N‑tillsats en förskjutning av vilka egenskaper som mest påverkade förnans nedbrytningshastighet. Sammanfattningsvis visar mina studier på vikten av genetisk mångfald för att främja växtartens stabilitet i miljöer som upplever antropogena förändringar.

No description available.

No description available.

Biomass energy is currently the largest renewable contributor to global energy supply and there is increasing demand for bioenergy feedstock. Consequently, the production of purpose-grown woody bioenergy crops, such as short rotation coppice (SRC) willow, is expected to proliferate. Although the economic and environmental benefits associated with SRC willow production are well documented, systematic assessments of nutrient cycling within these plantations are rare. The objective of this study was to examine biomass production and biogeochemical cycling of nitrogen (N), phosphorus (P), potassium (K), sulphur (S), calcium (Ca), and magnesium (Mg) during an initial four-year rotation of six willow varieties grown at four plantations along a 500 km north-south pedoclimatic gradient within Saskatchewan, Canada. Nutrient budgets were also calculated after quantifying various nutrient inputs (e.g., atmospheric deposition, soil mineral weathering, and organic matter mineralization), outputs (e.g., above- and below-ground biomass, leaching, and denitrification), and transfers (e.g., canopy exchange, leaf litter decomposition, and fine root turnover) affecting the plant available soil nutrient pool. Total stem, leaf litter, and below-ground (primarily fine roots) biomass production after four years averaged 19.0, 7.1, and 12.5 Mg ha-1, respectively, with corresponding soil nutrient budget deficits of 17, 39, 112, 271, and 74 kg ha-1 of N, P, K, Ca, and Mg, respectively, but a soil S surplus of 60 kg ha-1. Despite willow’s relatively low nutrient-demanding nature, negligible leaching and denitrification losses, and substantial nutrient cycling from leaf litter, the nutrient export in harvested biomass over multiple rotations will require soil nutrient amendments, particularly N and P, to maintain plantation productivity. Given the apparent eventual need for supplemental fertility to support adequate willow growth over the 22-yr plantation life span, the fate of broadcast 15N-labelled fertilizer was also examined. Though the willow accumulated less than ⅓ of the applied fertilizer N after one year, the majority of the residual fertilizer N (51%) remained available for willow uptake in subsequent years. Further research is needed to track the fate of applied fertilizers over multiple rotations to better understand fertilizer dynamics for optimizing SRC willow agronomy; thus helping to promote its viability as a biomass energy feedstock option.

No description available.