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Träfflista för sökning "WFRF:(Andresen Louise C. 1974) ;pers:(Rütting Tobias 1977)"

Sökning: WFRF:(Andresen Louise C. 1974) > Rütting Tobias 1977

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1.
  • Andresen, Louise C., 1974, et al. (författare)
  • Free amino acids in the rhizosphere
  • 2014
  • Ingår i: 19th European Nitrogen Cycle Meeting. September 10-12th 2014, Gent, Belgium.
  • Konferensbidrag (övrigt vetenskapligt/konstnärligt)
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2.
  • Andresen, Louise C., 1974, et al. (författare)
  • Patterns of free amino acids in tundra soils reflect mycorrhizal type, shrubification, and warming
  • 2022
  • Ingår i: Mycorrhiza. - : Springer Science and Business Media LLC. - 0940-6360 .- 1432-1890. ; 32:3-4, s. 305-313
  • Tidskriftsartikel (refereegranskat)abstract
    • The soil nitrogen (N) cycle in cold terrestrial ecosystems is slow and organically bound N is an important source of N for plants in these ecosystems. Many plant species can take up free amino acids from these infertile soils, either directly or indirectly via their mycorrhizal fungi. We hypothesized that plant community changes and local plant community differences will alter the soil free amino acid pool and composition; and that long-term warming could enhance this effect. To test this, we studied the composition of extractable free amino acids at five separate heath, meadow, and bog locations in subarctic and alpine Scandinavia, with long-term (13 to 24 years) warming manipulations. The plant communities all included a mixture of ecto-, ericoid-, and arbuscular mycorrhizal plant species. Vegetation dominated by grasses and forbs with arbuscular and non-mycorrhizal associations showed highest soil free amino acid content, distinguishing them from the sites dominated by shrubs with ecto- and ericoid-mycorrhizal associations. Warming increased shrub and decreased moss cover at two sites, and by using redundancy analysis, we found that altered soil free amino acid composition was related to this plant cover change. From this, we conclude that the mycorrhizal type is important in controlling soil N cycling and that expansion of shrubs with ectomycorrhiza (and to some extent ericoid mycorrhiza) can help retain N within the ecosystems by tightening the N cycle.
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3.
  • Andresen, Louise C., 1974, et al. (författare)
  • Amino acid and N mineralization dynamics in heathland soil after long-term warming and repetitive drought
  • 2015
  • Ingår i: Soil. - : Copernicus GmbH. - 2199-3971 .- 2199-398X. ; 1:1, s. 341-349
  • Tidskriftsartikel (refereegranskat)abstract
    • Monomeric organic nitrogen (N) compounds such as free amino acids (FAAs) are an important resource for both plants and soil microorganisms and a source of ammonium (NH4+) via microbial FAA mineralization. We compared gross FAA dynamics with gross N mineralization in a Dutch heathland soil using a 15N tracing technique. A special focus was made on the effects of climate change factors warming and drought, followed by rewetting. Our aims were to (1) compare FAA mineralization (NH4+ production from FAAs) with gross N mineralization, (2) assess gross FAA production rate (depolymerization) and turnover time relative to gross N mineralization rate, and (3) assess the effects of a 14 years of warming and drought treatment on these rates. The turnover of FAA in the soil was ca. 3 h, which is almost 2 orders of magnitude faster than that of NH4+ (i.e. ca. 4 days). This suggests that FAA is an extensively used resource by soil microorganisms. In control soil (i.e. no climatic treatment), the gross N mineralization rate (10 ± 2.9 μg N g−1 day−1) was 8 times smaller than the total gross FAA production rate of five AAs (alanine, valine, leucine, isoleucine, proline: 127.4 to 25.0 μg N g−1 day−1). Gross FAA mineralization (3.4 ± 0.2 μg N g−1 day−1) contributed 34% to the gross N mineralization rate and is therefore an important component of N mineralization. In the drought treatment, a 6–29% reduction in annual precipitation caused a decrease of gross FAA production by 65% and of gross FAA mineralization by 41% compared to control. On the other hand, gross N mineralization was unaffected by drought, indicating an increased mineralization of other soil organic nitrogen (SON) components. A 0.5–1.5 °C warming did not significantly affect N transformations, even though gross FAA production declined. Overall our results suggest that in heathland soil exposed to droughts a different type of SON pool is mineralized. Furthermore, compared to agricultural soils, FAA mineralization was relatively less important in the investigated heathland. This indicates more complex mineralization dynamics in semi-natural ecosystems.
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4.
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5.
  • Andresen, Louise C., 1974, et al. (författare)
  • Depolymerization and mineralization – investigating N availability by a novel 15N tracing model
  • 2016
  • Ingår i: SOIL. - : Copernicus GmbH. - 2199-398X. ; 2:3, s. 433-442
  • Tidskriftsartikel (övrigt vetenskapligt/konstnärligt)abstract
    • Depolymerization of soil organic matter such as proteins and peptides into monomers (e.g. amino acids) is currently thought to be the rate limiting step for N availability in terrestrial N cycles. The mineralization of free amino acids (FAA), liberated by depolymerization of peptides, is an important fraction of the total N mineralization. Accurate assessment 10 of peptide depolymerization and FAA mineralization rates is important in order to gain a better understanding of the N cycle dynamics. Due to the short time span, soil disturbance and unnatural high FAA content during the first few hours after the labelling with the traditional 15N pool dilution experiments, analytical models might overestimate peptide depolymerization rate. In this paper, we present an extended numerical 15N tracing model Ntrace which incorporates the FAA pool and related N processes in order to 1) provide a more robust and coherent estimation of production and mineralization rates of FAAs; 2) 15 and 2) suggest an amino acid N use efficiency (NUEFAA) for soil microbes, which is a more realistic estimation of soil microbial NUE compared to the NUE estimated by analytical methods. We compare analytical and numerical approaches for two forest soils; suggest improvements of the experimental work for future studies; and conclude that: i) FAA mineralization might be as equally an important rate limiting step for gross N mineralization as peptide depolymerization rate is, because about half of all depolymerized peptide N is consecutively being mineralized; and that ii) FAA mineralization and FAA 20 immobilization rates should be used for assessing NUEFAA.
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6.
  • Andresen, Louise C., 1974, et al. (författare)
  • Nitrogen dynamics after two years of elevated CO2 in phosphorus limited Eucalyptus woodland
  • 2020
  • Ingår i: Biogeochemistry. - : Springer Science and Business Media LLC. - 0168-2563 .- 1573-515X. ; 150, s. 297-312
  • Tidskriftsartikel (refereegranskat)abstract
    • It is uncertain how the predicted further rise of atmospheric carbon dioxide (CO2) concentration will affect plant nutrient availability in the future through indirect effects on the gross rates of nitrogen (N) mineralization (production of ammonium) and depolymerization (production of free amino acids) in soil. The response of soil nutrient availability to increasing atmospheric CO2 is particularly important for nutrient poor ecosystems. Within a FACE (Free-Air Carbon dioxide Enrichment) experiment in a native, nutrient poor Eucalyptus woodland (EucFACE) with low soil organic matter (≤ 3%), our results suggested there was no shortage of N. Despite this, microbial N use efficiency was high (c. 90%). The free amino acid (FAA) pool had a fast turnover time (4 h) compared to that of ammonium (NH4+) which was 11 h. Both NH4-N and FAA-N were important N pools; however, protein depolymerization rate was three times faster than gross N mineralization rates, indicating that organic N is directly important in the internal ecosystem N cycle. Hence, the depolymerization was the major provider of plant available N, while the gross N mineralization rate was the constraining factor for inorganic N. After two years of elevated CO2, no major effects on the pools and rates of the soil N cycle were found in spring (November) or at the end of summer (March). The limited response of N pools or N transformation rates to elevated CO2 suggest that N availability was not the limiting factor behind the lack of plant growth response to elevated CO2, previously observed at the site.
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7.
  • Andresen, Louise C., 1974, et al. (författare)
  • Simultaneous quantification of depolymerization and mineralization rates by a novel 15N tracing model
  • 2016
  • Ingår i: SOIL. - : Copernicus GmbH. - 2199-398X. ; 2, s. 433-442
  • Tidskriftsartikel (refereegranskat)abstract
    • The depolymerization of soil organic matter, such as proteins and (oligo-)peptides, into monomers (e.g. amino acids) is currently considered to be the rate-limiting step for nitrogen (N) availability in terrestrial ecosystems. The mineralization of free amino acids (FAAs), liberated by the depolymerization of peptides, is an important fraction of the total mineralization of organic N. Hence, the accurate assessment of peptide depoly- merization and FAA mineralization rates is important in order to gain a better process-based understanding of the soil N cycle. In this paper, we present an extended numerical 15 N tracing model Ntrace , which incorporates the FAA pool and related N processes in order to provide a more robust and simultaneous quantification of de- polymerization and gross mineralization rates of FAAs and soil organic N. We discuss analytical and numerical approaches for two forest soils, suggest improvements of the experimental work for future studies, and conclude that (i) when about half of all depolymerized peptide N is directly mineralized, FAA mineralization can be as important a rate-limiting step for total gross N mineralization as peptide depolymerization rate; (ii) gross FAA mineralization and FAA immobilization rates can be used to develop FAA use efficiency (NUEFAA), which can reveal microbial N or carbon (C) limitation.
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8.
  • Rütting, Tobias, 1977, et al. (författare)
  • Nitrogen cycle responses to elevated CO2 depend on ecosystem nutrient status
  • 2015
  • Ingår i: Nutrient Cycling in Agroecosystems. - : Springer Science and Business Media LLC. - 1385-1314 .- 1573-0867. ; 101:3, s. 285-294
  • Tidskriftsartikel (refereegranskat)abstract
    • Nitrogen (N) limitation of terrestrial ecosystems is a crucial factor for predicting how these ecosystems respond and feedback to climate change. Nitrogen availability for plants in terrestrial ecosystems depends on the internal soil N cycle and inputs to the ecosystem via biological N-2 fixation. We reviewed the effect of elevated atmospheric CO2 concentrations (eCO(2)) on gross soil N transformations to advance our understanding of ecosystem responses to eCO(2). Overall, neither gross mineralization nor gross nitrification was altered by eCO(2). However, emerging from ecosystem specific analysis, we propose a new conceptual model for eCO(2) effects on gross mineralization based on ecosystem nutrient status: gross mineralization is only stimulated in N limited ecosystems, but unaffected in phosphorus limited ecosystems. Moreover, the ratio of ammonium oxidation to immobilization is decreased under eCO(2), indicating a tighter N cycle with reduced ecosystem N losses. This new conceptual model on N cycle responses to eCO(2) should be tested in the future in independent experiments and it provides a new concept for refining mechanistic models of ecosystem responses to climate change.
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9.
  • Rütting, Tobias, 1977, et al. (författare)
  • Too little or not too little – gross nitrogen mineralization responses to elevated CO2
  • 2023
  • Ingår i: Advances in Ecological Research. - 0065-2504. ; 68, s. 51-62
  • Tidskriftsartikel (refereegranskat)abstract
    • Primary production is in many terrestrial ecosystems limited by the availability of nitrogen (N). Hence, ecosystems can sustain enhanced growth under global change only when sufficient N is available. Over time a progressive N limitation (PNL) of the response to elevated CO2 might develop. As the N availability for plants is strongly controlled by the internal recycling of N in soil, enhanced gross N mineralization is a potential mechanism to alleviate PNL. Based on meta-analysis we found that gross N mineralization is enhanced by elevated CO2 in N limited, but not in phosphorus limited ecosystems. As it is N limited ecosystems that are prone to PNL, the enhanced mineralization alleviates PNL. However, we found indication that the stimulation of gross N mineralization might diminish over time. More experiments on the soil N cycle in ecosystems exposed to elevated CO2 for decades are urgently needed to develop more robust knowledge. Global change is a multi-factor change. Elevated CO2 in combination with other global change factors led to antagonistic responses of gross N mineralization. This means that the response to combined treatments was not predicted by the sum of single treatment responses. As only few field experiments are multifactorial, there is a great need for more long-term field experiments with multiple global change factors. This meta-analysis highlights the need to study the complex soil N cycle in a holistic way, as different pathways of the N cycle responded differently to global change, complicating the interpretation of how N availability for plants might change.
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