Auswahl der wissenschaftlichen Literatur zum Thema „Microbial decomposers“
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Zeitschriftenartikel zum Thema "Microbial decomposers"
Lauber, Christian L., Jessica L. Metcalf, Kyle Keepers, Gail Ackermann, David O. Carter und Rob Knight. „Vertebrate Decomposition Is Accelerated by Soil Microbes“. Applied and Environmental Microbiology 80, Nr. 16 (06.06.2014): 4920–29. http://dx.doi.org/10.1128/aem.00957-14.
Der volle Inhalt der QuelleSiira-Pietikäinen, Anne, Janna Pietikäinen, Hannu Fritze und Jari Haimi. „Short-term responses of soil decomposer communities to forest management: clear felling versus alternative forest harvesting methods“. Canadian Journal of Forest Research 31, Nr. 1 (01.01.2001): 88–99. http://dx.doi.org/10.1139/x00-148.
Der volle Inhalt der QuelleBjelic, Dragana, Jelena Marinkovic, Branislava Tintor, Jordana Ninkov, Jovica Vasin, Milorad Zivanov und Snezana Jaksic. „Possibility of using Bacillus and Trichoderma strains for decomposition of crop residues“. Zbornik Matice srpske za prirodne nauke, Nr. 138 (2020): 51–59. http://dx.doi.org/10.2298/zmspn2038051b.
Der volle Inhalt der QuelleThormann, Markus N. „Diversity and function of fungi in peatlands: A carbon cycling perspective“. Canadian Journal of Soil Science 86, Special Issue (01.03.2006): 281–93. http://dx.doi.org/10.4141/s05-082.
Der volle Inhalt der QuellePan, Xu, Matty P. Berg, Olaf Butenschoen, Phil J. Murray, Igor V. Bartish, Johannes H. C. Cornelissen, Ming Dong und Andreas Prinzing. „Larger phylogenetic distances in litter mixtures: lower microbial biomass and higher C/N ratios but equal mass loss“. Proceedings of the Royal Society B: Biological Sciences 282, Nr. 1806 (07.05.2015): 20150103. http://dx.doi.org/10.1098/rspb.2015.0103.
Der volle Inhalt der QuelleHättenschwiler, Stephan, Nathalie Fromin und Sandra Barantal. „Functional diversity of terrestrial microbial decomposers and their substrates“. Comptes Rendus Biologies 334, Nr. 5-6 (Mai 2011): 393–402. http://dx.doi.org/10.1016/j.crvi.2011.03.001.
Der volle Inhalt der QuelleKuehn, Kevin A., Steven N. Francoeur, Robert H. Findlay und Robert K. Neely. „Priming in the microbial landscape: periphytic algal stimulation of litter-associated microbial decomposers“. Ecology 95, Nr. 3 (März 2014): 749–62. http://dx.doi.org/10.1890/13-0430.1.
Der volle Inhalt der QuelleD.J. RAJKHOWA und O. BORAH. „Effect of rice (Oryza sativa) straw management on growth and yield of wheat (Triticum aestivum)“. Indian Journal of Agronomy 53, Nr. 2 (10.10.2001): 112–15. http://dx.doi.org/10.59797/ija.v53i2.4843.
Der volle Inhalt der QuelleBatista, Daniela, Ahmed Tlili, Mark O. Gessner, Cláudia Pascoal und Fernanda Cássio. „Nanosilver impacts on aquatic microbial decomposers and litter decomposition assessed as pollution-induced community tolerance (PICT)“. Environmental Science: Nano 7, Nr. 7 (2020): 2130–39. http://dx.doi.org/10.1039/d0en00375a.
Der volle Inhalt der QuelleNugroho, Sutopo Ghani, Dermiyati, Jamalam Lumbanraja, Sugeng Triyono und Hanung Ismono. „Inoculation Effect of N2-Fixer and P-Solubilizer into a Mixture of Fresh Manure and Phosphate Rock Formulated as Organonitrofos Fertilizer on Bacterial and Fungal Populations“. JOURNAL OF TROPICAL SOILS 18, Nr. 1 (19.03.2013): 75. http://dx.doi.org/10.5400/jts.2013.v18i1.75-80.
Der volle Inhalt der QuelleDissertationen zum Thema "Microbial decomposers"
Dale, Sarah Elizabeth. „Leaf litter decomposition in tropical forests : disentangling leaf litter quality, soil nutrients, climate and microbial decomposers“. Thesis, Lancaster University, 2013. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.658223.
Der volle Inhalt der QuelleSanaei, Moghadam Fatemeh [Verfasser]. „Interactions between warming, nutrient enrichment and detritivores on litter decomposition and associated microbial decomposers / Fatemeh Sanaei Moghadam“. Kiel : Universitätsbibliothek Kiel, 2013. http://d-nb.info/1044294175/34.
Der volle Inhalt der QuelleWang, Ziming. „Les traits stoechiométriques microbiens : des outils pour comprendre et prédire les réponses des décomposeurs microbiens aux changements globaux“. Electronic Thesis or Diss., Université de Lorraine, 2023. http://www.theses.fr/2023LORR0098.
Der volle Inhalt der QuelleDecomposition of plant litter is one of the most important processes driving ecosystem functioning, it is the main energy and nutrient source in forested headwater streams. Any impairment of this process can have significant consequences for nutrient cycling. Decomposers, including aquatic hyphomycetes (AH) and heterotrophic bacteria, play a central role in decomposition, but their stoichiometric requirements and elemental plasticity remain understudied. While decomposers require inorganic nutrients to balance their stoichiometric requirements when breaking down nutrient-depleted plant litter, the specific optimal elemental ratios for species and communities of decomposers remain largely unknown. Results of different experimental studies carried out in controlled conditions first allowed to confirm the wide elemental plasticity of fungal biomass, both at the individual and at the assemblage/community scales. This plasticity appeared greater for phosphorus (P) than for nitrogen (N), and nutrient immobilisation occurred very quickly (observed for inorganic P after an 18h of nutrients addition). When evaluating leaf litter decomposition along N:P gradients, decomposer communities containing AH - but not bacteria alone - were able to maintain the decomposition process at high levels even at extremely low P contents and when N was sufficient, suggesting high capacities of AH to remobilise their internal P. Also, quantification of species relative abundances in AH assemblages suggested that individual stoichiometric traits participated to species distribution along the N:P gradient but were not sufficient to entirely explain assemblage structures. Contrary to common assumptions, while related to available N:P gradient, nutrient mineralisation (i.e. net release of inorganic nutrients from plant litter) remained limited, and nutrient immobilisation was the dominant process, at least for the duration of our experiments. Finally, both contaminants and temperature variations were able to significantly change the optimal N:P ratios for litter decomposition by decomposer communities, suggesting large - and potentially predictable - impacts of these stressors on the intensity and the dynamic of microbial decomposition of plant litter in ecosystems. All the results from these studies confirm that combining stoichiometric traits with other ecological and biological traits would certainly allow our understanding in depth, the decomposition process, and its response to global changes
Luitingh, Taryn Leigh. „Adaptation of the microbial decomposer community to the burial of skeletal muscle tissue in contrasting soils“. University of Western Australia. Centre for Forensic Science, 2008. http://theses.library.uwa.edu.au/adt-WU2009.0037.
Der volle Inhalt der QuelleDuarte, Sofia Alexandra Ferreira. „Biodiversity and activity of microbial decomposers of leaf litter in streams under anthropogenic stress“. Doctoral thesis, 2008. http://hdl.handle.net/1822/8602.
Der volle Inhalt der QuelleHuman activities are threatening biodiversity in freshwaters leading to irreversible alterations in ecosystem processes. One of the most important processes for the functioning of small-forested streams is the decomposition of allochthonous plant litter, which constitutes the major source of nutrients and energy for freshwater food-webs. Microbial decomposers, namely fungi and bacteria, play a critical role in this process degrading leaf material and increasing leaf palatability for invertebrate shredders. An obvious question that arises is in what extent pollution can affect the diversity of microbial decomposers altering the functions they perform in freshwater ecosystems. In a microcosm experiment, we showed that the loss of aquatic fungal species affected fungal biomass and reproduction, but not leaf mass loss. Complementarity effects appeared to occur between fungal species because multicultures had higher performances than those expected from individual performances in monocultures. Moreover, lower fungal biomass and leaf mass loss were found in the absence of Articulospora tetracladia and species identity affected all measured parameters. In a transplant experiment, we investigated how a community of microbial decomposers adapted to a reference site responds to a sudden decrease in the water quality. The transfer of leaves colonized at a reference site to a site with high concentration of nutrients and heavy metals in the stream water reduced fungal diversity and sporulation, but not fungal biomass and leaf decomposition. This suggests that high diversity of fungi may mitigated the impact of anthropogenic stress in streams. Most studies addressing microbial diversity on decomposing leaves rely on the microscopic identification of fungal conidia and on the number of bacterial morphotypes. However, the production of conidia by fungi varies with the species and it is affected by several environmental factors. On the other hand, bacteria have few morphological differences, making it difficult to accurately assess microbial diversity. In our work, DNA fingerprinting techniques were successfully used for assessing fungal and bacterial diversity. Denaturing gradient gel electrophoresis (DGGE) showed a more diverse microbial community on decomposing leaves than microscopic techniques. Moreover, DGGE allowed detecting shifts in microbial communities during leaf decomposition and under different stress conditions (eutrophication and metal pollution). The structure of fungal and bacterial communities on decomposing leaves changed along a gradient of inorganic nitrogen and phosphorus in streams, as indicated by canonical correspondence analysis based on the morphology of fungal conidia and on DNA fingerprinting. Sporulation was depressed in the most eutrophic streams, while bacterial biomass appeared to be stimulated, except in the presence of high nitrites and ammonium concentrations. Leaf decomposition rate was stimulated at only one site with moderate eutrophication. The exposure of naturally colonized leaves to environmentally realistic concentrations of copper and zinc alone or in mixtures showed that metal exposure altered the structure of fungal and bacterial communities on decomposing leaves. Exposure to metal mixtures or to the highest Cu concentration significantly reduced leaf decomposition rates and fungal reproduction, but not fungal biomass. Bacterial biomass was strongly inhibited by all metal treatments. Moreover, the combined effects of Cu and Zn on microbial decomposition of leaf litter were mostly additive, because observed effects did not differ from those expected as the sum of single metal effects. However, antagonistic effects on bacterial biomass were found in all metal combinations and on fungal reproduction in metal combinations with the highest Cu concentrations, particularly at longer exposure times. Moreover, the sequence by which metals were added to microcosms affected fungal biomass and sporulation, but not bacterial biomass, probably because microbial sensitivities to the metals were different. The resistance of microbial decomposers to Cu did not increase when communities were previously acclimated to Zn and vice-versa. Microbial decomposers could be expending considerable energy to maintain their functions under the stress imposed by the first metal and if so, species resistance might be diminished when the second metal was added. After release from metals, the structure of fungal communities became similar to that of control, as indicated by the principal response curves of sporulating species and also by the DGGE analyses. A recovery of the microbial activity seemed also to occur, as shown by the lack of differences in leaf mass loss, bacterial biomass and fungal reproduction between control and metal treatments.
As actividades humanas estão a ameaçar a biodiversidade dos ecossistemas aquáticos, conduzindo a alterações irreversíveis no seu funcionamento. Um dos processos mais importantes para o funcionamento dos ecossistemas de rios de baixa ordem é a decomposição de detritos vegetais alóctones, que constituem a principal fonte de carbono e energia para as cadeias alimentares nesses sistemas de água doce. Os microrganismos decompositores aquáticos, nomeadamente os fungos e as bactérias, desempenham um papel fundamental na decomposição dos detritos vegetais e aumentam a sua palatabilidade para os invertebrados trituradores. Uma questão relevante no âmbito da Ecologia actual é a de saber se a poluição afecta a biodiversidade e quais os impactos para o funcionamento dos ecossistemas aquáticos. Numa experiência em microcosmos, mostrámos que a perda de espécies de fungos aquáticos afectava a biomassa e a reprodução dos fungos, mas não a decomposição de folhada. As espécies de fungos pareceram exibir efeitos de complementaridade uma vez que as culturas mistas tiveram desempenhos superiores ao esperado a partir dos desempenhos em cultura pura. Contudo, a identidade das espécies afectou todos os parâmetros analisados. Além disso, a biomassa dos fungos e a perda de massa foliar foram menores na ausência de Articulospora tetracladia. Numa experiência de transplante de folhas entre rios, investigámos como uma comunidade de microrganismos decompositores adaptados a um local de referência responde a um declínio abrupto na qualidade da água. A transferência de folhas colonizadas num local de referência para um local com concentrações elevadas de nutrientes e metais pesados na água reduziu a diversidade e a esporulação dos fungos, mas não a sua biomassa e a decomposição foliar. Isto sugere que uma elevada diversidade de fungos pode contribuir para atenuar o impacto de stressores antropogénicos nos rios. A maioria dos estudos efectuados tem analisado a diversidade de microrganismos associados a folhas em decomposição com base na identificação microscópica das conídias libertadas pelos fungos e nos tipos morfológicos de bactérias. No entanto, a produção de conídias pelos fungos varia com a espécie e é afectada por vários factores ambientais. Por outro lado, as bactérias possuem poucas diferenças morfológicas entre si, tornando difícil avaliar com exactidão a diversidade microbiana. No nosso trabalho, a electroforese em gradiente desnaturante (DGGE) do DNA microbiano mostrou uma comunidade de fungos e de bactérias mais diversa em folhas em decomposição do que as técnicas de microscopia. O DGGE permitiu detectar alterações na estrutura das comunidades durante a decomposição foliar e em diferentes condições de stresse (eutrofização e poluição por metais). A estrutura das comunidades de fungos e de bactérias nas folhas em decomposição sofreu alterações ao longo de um gradiente de azoto e de fósforo nos rios, como indicado pelas análises de correspondência canónica baseadas na morfologia das conídias dos fungos e no perfil de DGGE. A esporulação diminuiu nos rios mais eutrofizados, enquanto que a biomassa de bactérias pareceu ser estimulada, excepto na presença de concentrações elevadas de nitritos e amónia. A taxa de decomposição foliar foi estimulada apenas num dos locais com eutrofização moderada. A exposição de folhas colonizadas naturalmente a concentrações de cobre e de zinco, ambientalmente realísticas, alterou a estrutura das comunidades de fungos e de bactérias nas folhas em decomposição. A exposição às misturas de metais ou à concentração de Cu mais elevada reduziu significativamente a taxa de decomposição foliar e a reprodução dos fungos, mas não inibiu a biomassa dos fungos. A biomassa bacteriana foi inibida em todos os tratamentos com metais. Além disso, os efeitos combinados do Cu e do Zn na decomposição microbiana da folhada foram maioritariamente aditivos, uma vez que os efeitos observados não diferiram dos esperados a partir da soma dos efeitos de cada metal isolado. No entanto, foram observados efeitos antagonísticos na biomassa de bactérias, em todas as combinações de metais, e na reprodução de fungos nas combinações contendo Cu na concentração mais elevada, particularmente em tempos mais longos de exposição. A sequência pela qual os metais foram adicionados aos microcosmos afectou a biomassa e a esporulação dos fungos, mas não a biomassa das bactérias provavelmente porque a sensibilidade dos microrganismos aos dois metais era diferente. A resistência dos microrganismos decompositores ao Cu não aumentou quando as comunidades foram previamente aclimatadas ao Zn e vice-versa. Os microrganismos poderiam estar a consumir uma fracção de energia considerável para manter as suas funções na presença do primeiro metal e, por este motivo, a sua resistência poderia estar diminuída quando o segundo metal foi adicionado. Após libertação do stresse metálico, a estrutura das comunidades de fungos tornou-se semelhante à das comunidades controlo, como indicado pelas curvas de resposta principal das espécies identificadas a partir dos esporos e pela análise de DGGE. Além disso, a actividade microbiana pareceu recuperar após a libertação do stresse metálico, como sugerido pela ausência de diferenças na perda de massa foliar, na biomassa das bactérias e na reprodução dos fungos entre o controlo e os tratamentos com metais.
Fundação para a Ciência e a Tecnologia (FCT) - SFRH/BD/13482/2003.
Torres, Cristina Alexandra Salgado. „Microbial decomposers diversity and litter decomposition along an altitudinal gradient in tropical and temperate stream ecosystems“. Master's thesis, 2015. http://hdl.handle.net/10316/32177.
Der volle Inhalt der QuelleA taxa de decomposição microbiana de folhas senescentes em rios e a riqueza em taxa de fungos e bactérias aquáticas foram estudados ao longo de um gradiente de altitude em dois sistemas, 1600-3800 m snm no Equador (ecossistema tropical a 0 ° Lat) e 1992-3200 m snm em Colorado EUA (ecossistema temperado a 40 ° N). Sacos de malha fina (0,5 mm) contendo folhas de amieiro nativo em cada una das zonas (Equador: Alnus acuminata Kunth; Colorado: Alnus incana (L.) Moench) foram incubadas em cinco locais ao longo do gradiente de altitude em cada latitude e recuperados em datas de amostragem selecionados para determinar as taxas de decomposição e a diversidade de decompositores. As taxas de decomposição (k) foram mais rápidos em Colorado (0,0197-0,0453 gama de valores) do que no Equador (0,0065 - 0.014). No Equador a decomposição diminuiu com a elevação (regressão linear, p <0,001; R2 = 0.95), o que foi explicado pela diferença de temperatura entre locais. Em Colorado a decomposição não mudo com a altitude (regressão linear, p = 0,48; R2 <0,001) e não esteve ligada a nenhum dos parâmetros ambientais registrados. Os nitratos no Colorado foram ~ 30 vezes mais elevada do que no Equador (11,28 vs 0,40 mg / L; t-test, p = 0.04) podendo o seu efeito sobrepor-se ao da temperatura. A diversidad de microrganismos decompositores foi estimada aplicando a eletroforese em gel com gradiente desnaturante (DGGE), avaliando o DNA ribossomal (rDNA) para fungos aquático (região ITS2) e bactérias (V3 região variável). A diversidade de fungos aquáticos no Equador aumentou com a elevação (regressão linear, p = 0.03; R2 = 0.83), enquanto no Colorado o número máximo de taxa atingiu um pico em altitudes médias (regressão polinomial; p = 0.7; R2 = 0.57). Os três primeiros eixos de uma “análise de componentes principais” (PCA) no Equador explicaram 93% da variabilidade total e o número de OTUs em fungos esteve relacionada com PO4, que foi maior nos locais mais altos e desceu para os locais mais baixos. No Colorado, os três eixos da PCA explicaram 92% da variabilidade total e a riqueza de taxa foi relacionada com CPOM, baixa profundidade da água e concentrações moderadas de NO3. O número de taxa para fungos registrados no Equador e no Colorado (13.3 e 15.2 OTUs) não foi estatisticamente diferente (teste t; p = 0.2; t = 1.43; df = 8). A análise MDS usando o coeficiente de similaridade de Bray-Curtis mostrou que a identidade dos OTUs em Colorado e Equador foi diferente. As unidades taxonómicas das bactérias no Equador e Colorado diminuiu com a altitude (regressão linear; p = 0,0001; R2 = 0.58 e p = 0.0004; R2 = 0.99, respetivamente). O maior número de OTUs ao longo do gradiente equatoriana foi correlacionado principalmente com o segundo eixo do PCA, que por sua vez se correlaciona com CPOM, NO3 e NO2. Em Colorado a variabilidade dos taxa foi negativamente correlacionada com o primeiro eixo do PCA, o qual foi correlacionado principalmente com concentrações de temperatura e NO3. A comunidade das bactérias exibiu uma distribuição cosmopolita, i.e., não houve diferenças na identidade entre Equador e Colorado (MDS; stress value: 0.19). A dissimilaridade entre as comunidades ao longo dos gradientes de altitude (β diversidade) foi menor no Equador do que em Colorado para fungos aquáticos (ANOSIM, p = 0.51; global R = 0.004 vs p = 0.003; global R = 0.54) e bactérias (ANOSIM, p = 0.54; R = -0.021 global vs. p = 0.003; global R = 0.51). Estes resultados sugerem que (1) A taxa de decomposição é um processo dependente da temperatura, mas que pode ser mascarada por outros fatores, tais como nutrientes na água. (2) A riqueza de espécies e a composição da comunidade de microrganismos decompositores pode ser controlada por variáveis ambientais locais, como os nutrientes dissolvidos na água e características de substrato (qualidade das folhas), o que sugere que os padrões observados em organismos de grandes dimensões pode não afetar aos organismos de menor tamanho. Além disso, a riqueza latitudinal de espécies pode ser dificilmente observada ao longo de um gradiente de altitude, caso a temperatura seja o principal fator ambiental que controla a diversidade e o turnover de espécies, uma vez que as alterações térmicas na água são menores do que for a dela.
The microbial decomposition rate and species richness of aquatic fungi and bacteria were studied along an altitudinal gradient from 1600 to 3800 m.a.s.l. in Ecuador (tropical ecosystem at 0° Lat) and from 1992 to 3200 m.a.s.l. in Colorado US (temperate ecosystem at 40°N). Fine mesh bags (0.5 mm) containing native alder leaves from tropical (Alnus acuminata Kunth) and temperate (Alnus incana (L.) Moench) zones were incubated in five locations along the altitudinal gradient at each latitude and retrieved at selected sampling dates to decomposition rates and diversity of decomposers. Decomposition rates (k) were faster in Colorado (0.0197 - 0.0453 range) than in Ecuador (0.0065 - 0.014 range). In Ecuador litter decomposition decreased with elevation (linear regression, p < 0.001; R2 = 0.95), which was explained by temperature difference across sites. In Colorado litter decomposition did not change with altitude (linear regression, p = 0.48; R2 < 0.001) and was not related to any of the measured environmental parameters. Nitrates in Colorado were ~30 fold higher than in Ecuador (11.28 vs. 0.40 μg/L; t-test, p = 0.04) and might be overridden the temperature effect. Microbial decomposers diversity was estimated applying the denaturing gradient gel electrophoresis (DGGE) technique and assessing the ribosomal DNA (rDNA) for aquatic fungi (ITS2 region) and bacteria (V3 variable region). Aquatic fungi diversity in Ecuador increased with elevation (linear regression, p = 0.03; R2 = 0.83), whereas in Colorado the maximum number of taxa peaked at middle altitudes (polynomial regression; p = 0.7; R2 = 0.57). The three PCA axis in Ecuador explained 93% of the total variability and the number of fungal OTUs related with PO4. In Colorado, the three PCA axis explained 92% of the total variability and taxa richness was related with CPOM standing stock, shallow waters and moderate concentrations of NO3. The number of fungal taxa recorded in Ecuador and Colorado (13.3 and 15.2 OTUs) was not statistically different (t-test; p = 0.2; t =1.43; df = 8). The MDS analysis using Bray-Curtis similarity coefficient determined that fungi taxa is biogeographically distributed by latitude. Bacteria taxa units in Ecuador and Colorado decreased with altitude (linear regression; p = 0.0001; R2 = 0.58 and p = 0.0004; R2 = 0.99). The higher number of OTUs along the Ecuadorian gradient was primarily correlated with the 2nd PCA axis, which in turn was correlated with CPOM standing stock, NO3 and NO2. In Colorado the taxa variability was negatively correlated with the first PCA axis, which was mainly correlated with temperature and NO3 concentrations. Bacteria community exhibited a cosmopolitan distribution (MDS; stress value: 0.19). The dissimilarity among communities along the altitudinal gradients (β diversity) was lower in Ecuador than in Colorado for aquatic fungi (ANOSIM, p = 0.51; Global R= 0.004 vs. p = 0.003; Global R= 0.54) and bacteria (ANOSIM, p = 0.54; Global R= -0.021 vs. p = 0.003; Global R= 0.51). These results suggest that (1) litter decomposition is a temperature dependent process, which can be overridden by other factors such as nutrients in the water. (2) Species richness and the community composition of microbial decomposers may be controlled by local environmental variables, such as dissolved nutrients in water and substrate characteristics (leaf quality), which may imply that broadly patterns observed on large organisms might not affect small size organisms. Besides, latitudinal species richness tendency might be barely observed along an altitudinal gradient, considering the temperature as the mainly environmental factor driving the diversity and the taxa turnover.
Roy, Shamik. „Soil microorganisms and biogeochemical cycles in a grazing ecosystem: interactions between producers, consumers, and decomposers“. Thesis, 2020. https://etd.iisc.ac.in/handle/2005/5073.
Der volle Inhalt der QuelleBuchteile zum Thema "Microbial decomposers"
Kora, Aruna Jyothi. „Applications of Waste Decomposer in Plant Health Protection, Crop Productivity and Soil Health Management“. In Environmental and Microbial Biotechnology, 609–24. Singapore: Springer Singapore, 2022. http://dx.doi.org/10.1007/978-981-16-2225-0_22.
Der volle Inhalt der QuelleBraunbeck, Helga G. „Lichen“. In Microbium, 81–97. Earth, Milky Way: punctum books, 2023. http://dx.doi.org/10.53288/0396.1.07.
Der volle Inhalt der QuellePascoal, Cláudia, Isabel Fernandes, Sahadevan Seena, Michael Danger, Verónica Ferreira und Fernanda Cássio. „Linking Microbial Decomposer Diversity to Plant Litter Decomposition and Associated Processes in Streams“. In The Ecology of Plant Litter Decomposition in Stream Ecosystems, 163–92. Cham: Springer International Publishing, 2021. http://dx.doi.org/10.1007/978-3-030-72854-0_9.
Der volle Inhalt der QuelleBildstein, Keith L. „Essential Ecology of Scavengers“. In Vultures of the World, 12–19. Cornell University Press, 2022. http://dx.doi.org/10.7591/cornell/9781501761614.003.0002.
Der volle Inhalt der QuelleLavelle, Patrick. „Biological basis of soil organic carbon sequestration: a complex set of interactive processes“. In Understanding and fostering soil carbon sequestration, 83–114. Burleigh Dodds Science Publishing, 2022. http://dx.doi.org/10.19103/as.2022.0106.04.
Der volle Inhalt der QuelleCohen, Andrew S. „Paleolimnology: The Past Meets the Future“. In Paleolimnology. Oxford University Press, 2003. http://dx.doi.org/10.1093/oso/9780195133530.003.0019.
Der volle Inhalt der QuelleDharani, L., R. Umapriya, J. Rohan, G. Surendran und P. Deepak. „Microbes and wastewater treatment“. In Clean Technologies Toward the Development of a Sustainable Environment and Future, 1–17. IWA Publishing, 2023. http://dx.doi.org/10.2166/9781789063783_0001.
Der volle Inhalt der QuelleSheikhavandi, Tarlan. „Microbial Functional Activity in Bioremediation of Contaminated Soil and Water“. In Handbook of Research on Uncovering New Methods for Ecosystem Management through Bioremediation, 286–315. IGI Global, 2015. http://dx.doi.org/10.4018/978-1-4666-8682-3.ch012.
Der volle Inhalt der QuelleRansom, Michel D., Charles W. Rice, Timothy C. Todd und William A. Wehmueller. „Soils and Soil Biota“. In Grassland Dynamics, 48–66. Oxford University PressNew York, NY, 1998. http://dx.doi.org/10.1093/oso/9780195114867.003.0004.
Der volle Inhalt der Quelle„Metabolites of Lactic Acid Bacteria (LAB): Production, Formulation and Potential applications in Food Industries“. In Prospective Research and Technological Advancements in Food and Health Sciences, 139–228. Skyfox Publishing Group, 2023. http://dx.doi.org/10.22573/spg.023.978-93-90357-07-9/6.
Der volle Inhalt der QuelleKonferenzberichte zum Thema "Microbial decomposers"
Waluyo, Lud. „Antagonism of Microbial Consortium Decomposers in Deadly Water-borne Pathogens in Domestic Wastewater“. In 2018 3rd International Conference on Education, Sports, Arts and Management Engineering (ICESAME 2018). Paris, France: Atlantis Press, 2018. http://dx.doi.org/10.2991/amca-18.2018.168.
Der volle Inhalt der QuelleWaluyo, Lud. „The Consortium of Microbial Decomposers on Heavy Metal Resistant Waste to Improve Environmental Health“. In International Conference on Community Development (ICCD 2020). Paris, France: Atlantis Press, 2020. http://dx.doi.org/10.2991/assehr.k.201017.088.
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