Auswahl der wissenschaftlichen Literatur zum Thema „Nutrient cycling“

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Zeitschriftenartikel zum Thema "Nutrient cycling"

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van Breemen, Nico. „Nutrient cycling strategies“. Plant and Soil 168-169, Nr. 1 (Januar 1995): 321–26. http://dx.doi.org/10.1007/bf00029344.

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MAHENDRAPPA, M. K., N. W. FOSTER, G. F. WEETMAN und H. H. KRAUSE. „NUTRIENT CYCLING AND AVAILABILITY IN FOREST SOILS“. Canadian Journal of Soil Science 66, Nr. 4 (01.11.1986): 547–72. http://dx.doi.org/10.4141/cjss86-056.

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Nutrient availability in different forest soils must be known before increased wood production can be sustained either by adding supplemental nutrients or by judicious silvicultural operations to optimize the linkage between the variable nutrient requirements of forest crops. This is complicated by the variable availability of nutrients on forest sites during crop development. Forest crops unlike agricultural crops have long rotation periods which make it difficult to apply agricultural methods of estimating potentially available nutrients directly to forest soils. Presented in this review are (i) various approaches used in forestry to estimate the nutrient supplying potential of different sites, (ii) factors affecting nutrient availability, and (iii) evidence to suggest that nutrient cycling processes in forest ecosystems are important factors affecting tree growth. It is suggested that data from chemical analyses of soil samples collected at specific times and sites should be used with caution for both practical decision making and simulation modelling purposes. Key words: Nitrogen, phosphorus, litterfall, throughfall, stemflow, mineralization
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Santos, Perlon Maia dos, Antonio Clementino dos Santos, Durval Nolasco das Neves Neto, Wallace Henrique de Oliveira, Luciano Fernandes Sousa und Leonardo Bernardes Taverny de Oliveira. „Implementation of Silvopastoral Systems under Nutrient Cycling in Secondary Vegetation in the Amazon“. Journal of Agricultural Science 10, Nr. 4 (05.03.2018): 124. http://dx.doi.org/10.5539/jas.v10n4p124.

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Silvopastoral systems can be implemented in idle secondary forests; however, they may affect nutrient cycling in these ecosystems. This farming practice using babassu palms (Attalea speciosa Mart.) and Mombasa grass (Panicum maximum Jacq.) has been little studied, and the nutrient cycling occurred during this practice is yet unknown. The goal of this paper was to detect the leaf litter accumulation, decomposition, and nutrient release occurring in silvopastoral systems in a babassu secondary forest, and compared the results with those of a native forest and of a pasture grown under full sunlight. The data relating to deposition, chemical composition, decomposition, and macronutrient release of leaf litter and pasture litter were evaluated by multivariate analyses. The results showed that forest thinning reduced leaf litter deposition and overall nutrient cycling but had no effect on decomposition rates. Conversely, the presence of grass in the understory promoted increased overall nutrient cycling rates. The cycling in integrated systems occurs more similar to that of forests than that of monocultures. The greater the thinning intensity the more similar the cycling will be relative to that occurring in pastures and in monocultures. The nutrients Ca, Mg, and N were the most affected by thinning. Moreover, the presence of grass in integrated systems provided an increased N and Mg cycling, whereas the thinning reduced Ca cycling. K showed the highest release and return ratio to the soil. Lastly, leaf litter from pasture areas showed higher contents of nutrients, decomposition rates, as well as an enhanced nutrient cycling capacity.
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Macedo, Priscila Helena da Silva, Emily Mariano da Cruz Lopes, Mariano Vieira dos Santos de Souza Lopes, Fernando César Sala und Claudinei Fonseca Souza. „Macronutrient cycling in hydroponic lettuce cultivation“. Ambiente e Agua - An Interdisciplinary Journal of Applied Science 17, Nr. 5 (04.10.2022): 1–11. http://dx.doi.org/10.4136/ambi-agua.2849.

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In order to address issues of limited resources and contamination by fertilizers, nutrient solutions may be reused in hydroponics as an alternative to their disposal in the environment. This work evaluated the feasibility of nutrient replacement for the nutrient solutions reused during lettuce hydroponic cultivation. The experiment was carried out in an agricultural greenhouse in an NFT hydroponic system using the “Milena” lettuce cultivar. The experiment was divided into two stages: 1) monitoring and data collection and proposition of nutrient replacement management; and 2) validation of the proposed replacement management. Monitoring the consumption of the crop's nutritional solution in the first stage served as the basis for the proposed nutritional replacement management. Management was validated in the second stage through the evaluation of fresh and dry mass, crop nutritional status, and the amount of the fertilizer applied in the treatments: T1 - nutrient replacement with nutrient solution reuse; and T2 - nutrient replacement without nutrient solution reuse. The fresh and dry mass data and the amount of nutrients absorbed by the plants were submitted to the t-test at 5% probability, showing no significant difference between the treatments, making it possible to conclude that the nutrient solution reuse provided nutrient replacement during the lettuce crop cultivation. Keywords: hydroponic system, Lactuca sativa L., macronutrient rational use.
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Rogers, Howard M. „Litterfall, decomposition and nutrient release in a lowland tropical rain forest, Morobe Province, Papua New Guinea“. Journal of Tropical Ecology 18, Nr. 3 (26.03.2002): 449–56. http://dx.doi.org/10.1017/s0266467402002304.

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The analysis of litter quantity, litter decomposition and its pattern of nutrient release is important for understanding nutrient cycling in forest ecosystems. Plant growth and maintenance are partly met through nutrient cycling (O'Connell & Sankaran 1997) which is dominated by litter production and decomposition. Litter fall is a major process for transferring nutrients from above-ground vegetation to soils (Vitousek & Sanford 1986), while decomposition of litter releases nutrients (Maclean & Wein 1978). The rate at which nutrients are recycled influences the net primary productivity of a forest. Knowledge of these processes from tropical rain forests is relatively poor (O'Connell & Sankaran 1997), and in particular there are no known published studies on nutrient cycling from lowland tropical forests in Papua New Guinea. The few studies from Papua New Guinea are confined to the mid-montane forest zone (Edwards 1977, Edwards & Grubb 1982, Enright 1979, Lawong et al. 1993).
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Anderson, Wendy B., und William G. Eickmeier. „Nutrient resorption in Claytonia virginica L.: implications for deciduous forest nutrient cycling“. Canadian Journal of Botany 78, Nr. 6 (01.06.2000): 832–39. http://dx.doi.org/10.1139/b00-056.

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According to the vernal dam hypothesis, spring ephemeral herbs temporarily sequester large nutrient pools in deciduous forests prior to canopy closure and return the nutrients to the soil following senescence of aboveground tissues. However, many species resorb nutrients from their leaves back to belowground tissues during senescence, and the degree of resorption is often associated with soil nutrient availability. Species that store large proportions of their absorbed nutrients between years are not participating in the temporary sequestering and rapid recycling of nutrients implied by the vernal dam. We investigated the extent to which Claytonia virginica L. sequestered and returned nutrients to the soil in response to nitrogen (N) and phosphorus (P) availability. We tested the effect of nutrient availability on nutrient use efficiency, resorption efficiency, and resorption proficiency (% nutrient in senescent leaves) of Claytonia. Nutrient additions significantly decreased N but not P use efficiency of Claytonia, particularly as the growing season progressed. Nutrient additions also significantly reduced N resorption efficiency from 80 to 47% and decreased P resorption efficiency from 86 to 56%. N and P resorption proficiencies were also significantly lower in senesced leaves of fertilized plants: N concentrations were 2.33% when unfertilized and 4.13% when fertilized, while P concentrations were 0.43% when unfertilized versus 0.57% when fertilized. When unfertilized, Claytonia was more efficient at resorption compared with other spring herbs, but similar to other species when fertilized. However, Claytonia was much less proficient in resorbing nutrients than other reported plants, because senescent tissues maintained substantially higher concentrations of N and P, particularly when fertilized. In conclusion, Claytonia, an important spring ephemeral species, exhibits physiological responses that emphasize its role in the vernal dam by its temporary sequestration and substantial, rapid return of nutrients in deciduous forests. Adding nutrients to the site increases the total mass and the relative proportion of nutrients that Claytonia returns to the soil rather than sequestering between seasons, which ultimately increases nutrient recycling rates within the entire system.Key words: Claytonia virginica, nutrient response, resorption efficiency, nutrient cycling, spring ephemerals, vernal dam.
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Saravanan, S., C. Buvaneswaran, P. Manivachagam, K. Rajagopal und M. George. „Nutrient cycling in Casuarina (Casuarina equisetifolia) based agroforestry system“. Indian Journal of Forestry 35, Nr. 2 (01.06.2012): 187–91. http://dx.doi.org/10.54207/bsmps1000-2012-apbnt4.

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The present report gives an account of the results of research carried out on litter production, accumulation and nutrient return through rainfall, stem flow, throughfall and interception to soil litter fall, under Casuarina-Black Gram Agroforestry Models (age 4 years, density 650 trees/ha). It was found that of the total rainfall (497.9 mm) 1.2% was recorded as stem flow and 80% as throughfall while the interception accounted for 19 %. It is found that on an average annual basis, of the total uptake of various nutrients was retained in the non-photosynthetic biomass and the rest returned to soil. These results show that among the nutrients, maximum annual retention was accounted for potassium while, the minimum for nitrogen. This paper deals the nutrient accumulation in standing crop, nutrient concentration and return, rainfall interception, nutrient concentration in rain wash, nutrient return through rain wash and Nutrient retained, returned and uptake (kg/ha/yr) in Casuarina under Agroforestry System in detail.
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BROWN, DENNIS H., und JEFFREY W. BATES. „Bryophytes and nutrient cycling“. Botanical Journal of the Linnean Society 104, Nr. 1-3 (September 1990): 129–47. http://dx.doi.org/10.1111/j.1095-8339.1990.tb02215.x.

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ATTIWILL, PETER M., und MARK A. ADAMS. „Nutrient cycling in forests“. New Phytologist 124, Nr. 4 (August 1993): 561–82. http://dx.doi.org/10.1111/j.1469-8137.1993.tb03847.x.

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L�ng, I. „Nutrient cycling and sustainability“. Fertilizer Research 43, Nr. 1-3 (1996): 31–35. http://dx.doi.org/10.1007/bf00747679.

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Dissertationen zum Thema "Nutrient cycling"

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Ngai, Zoology. „Trophic effects on nutrient cycling“. Thesis, University of British Columbia, 2008. http://hdl.handle.net/2429/2851.

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The top-down effects of consumers and bottom-up effects of resource availability are important in determining community structure and ecological processes. I experimentally examined the roles of consumers — both detritivores and predators — and habitat context in affecting nutrient cycling using the detritus-based insect community in bromeliad leaf wells. I also investigated the role of multiple resources in limiting plant productivity using meta analyses. The insect community in bromeliads only increased nitrogen release from leaf detritus in the presence of a predator trophic level. When only detritivores were present, the flow of stable isotope-labeled nitrogen from detritus to bromeliads was statistically indistinguishable from that in bromeliads lacking insects. I suggest that emergence of adult detritivores constitutes a loss of nitrogen from bromeliad ecosystems, and that predation reduces the rate of this nutrient loss. Hence, insects facilitate nutrient uptake by the plant, but only if both predators and detritivores are present. Moreover, predators can affect nutrient cycling by influencing the spatial scale of prey turnover. This mechanism results in a pattern opposite to that predicted by classic trophic cascade theory. Increasing habitat complexity can have implications for nutrient cycling by decreasing the foraging efficiency of both predators and their prey, and by affecting the vulnerability of predators to intraguild predation. Along a natural gradient in bromeliad size, I found that, depending on the relationship between community composition and habitat size, habitat complexity interacts with the changing biotic community to either complement or counteract the impact of predators on nutrient uptake by bromeliads. In contrast to the existing emphasis on single-resource limitation of primary productivity, meta-analyses of a database of 653 studies revealed widespread limitation by multiple resources, and frequent interaction between these resources in restricting plant growth. A framework for analyzing fertilization studies is outlined, with explicit consideration of the possible role of multiple resources. I also review a range of mechanisms responsible for the various forms of resource limitation that are observed in fertilization experiments. These studies emphasize that a wider range of predator and nutrient impacts should be considered, beyond the paradigm of single resource limitation or classic trophic cascades.
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Barthelemy, Hélène. „Herbivores influence nutrient cycling and plant nutrient uptake : insights from tundra ecosystems“. Doctoral thesis, Umeå universitet, Institutionen för ekologi, miljö och geovetenskap, 2016. http://urn.kb.se/resolve?urn=urn:nbn:se:umu:diva-120191.

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Reindeer appear to have strong positive effects on plant productivity and nutrient cycling in strongly nutrient-limited ecosystems. While the direct effects of grazing on vegetation composition have been intensively studied, much less is known about the indirect effect of grazing on plant-soil interactions. This thesis investigated the indirect effects of ungulate grazing on arctic plant communities via soil nutrient availability and plant nutrient uptake. At high density, the deposition of dung alone increased plant productivity both in nutrient rich and nutrient poor tundra habitats without causing major changes in soil possesses. Plant community responses to dung addition was slow, with a delay of at least some years. By contrast, a 15N-urea tracer study revealed that nutrients from reindeer urine could be rapidly incorporated into arctic plant tissues. Soil and microbial N pools only sequestered small proportions of the tracer. This thesis therefore suggests a strong effect of dung and urine on plant productivity by directly providing nutrient-rich resources, rather than by stimulating soil microbial activities, N mineralization and ultimately increasing soil nutrient availability. Further, defoliation alone did not induce compensatory growth, but resulted in plants with higher nutrient contents. This grazing-induced increase in plant quality could drive the high N cycling in arctic secondary grasslands by providing litter of a better quality to the belowground system and thus increase organic matter decomposition and enhance soil nutrient availability. Finally, a 15N natural abundance study revealed that intense reindeer grazing influences how plants are taking up their nutrients and thus decreased plant N partitioning among coexisting plant species. Taken together these results demonstrate the central role of dung and urine and grazing-induced changes in plant quality for plant productivity. Soil nutrient concentrations alone do not reveal nutrient availability for plants since reindeer have a strong influence on how plants are taking up their nutrients. This thesis highlights that both direct and indirect effects of reindeer grazing are strong determinants of tundra ecosystem functioning. Therefore, their complex influence on the aboveground and belowground linkages should be integrated in future work on tundra ecosystem N dynamic.
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Heggenstaller, Andrew Howard. „Productivity and nutrient cycling in bioenergy cropping systems“. [Ames, Iowa : Iowa State University], 2008.

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Lammers, Peter J. „Energy and nutrient cycling in pig production systems“. [Ames, Iowa : Iowa State University], 2009.

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Jabro, Nicholas Berman. „Microcosm studies of nutrient cycling in Bahamian stromatolites“. College Park, Md.: University of Maryland, 2008. http://hdl.handle.net/1903/8594.

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Thesis (M.S.) -- University of Maryland, College Park, 2008.
Thesis research directed by: Marine, Estuarine, Environmental Sciences Graduate Program. Title from t.p. of PDF. Includes bibliographical references. Published by UMI Dissertation Services, Ann Arbor, Mich. Also available in paper.
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Langi, Martina Agustina. „Nutrient cycling in tropical plantations and secondary rainforests /“. St. Lucia, Qld, 2001. http://www.library.uq.edu.au/pdfserve.php?image=thesisabs/absthe16357.pdf.

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McManamay, Ryan A. „The effect of resource stoichiometry on fish and macroinvertebrate nutrient excretion“. Thesis, Virginia Tech, 2007. http://hdl.handle.net/10919/30780.

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Consumer-driven nutrient cycling has been shown to be an important process in supplying inorganic nutrients to autotrophic and heterotrophic organisms in aquatic ecosystems. Theory indicates that consumer nutrient excretion is influenced primarily by an organismâ s nutrient composition; however, an organismâ s diet should also play an important role in nutrient excretion, especially if the consumer is nutrient limited. This study asks the question, how does diet influence nutrient excretion of consumers at different trophic levels? Macroinvertebrates and fish were collected from six streams and nitrogen (N) and phosphorus (P) excretion were quantified. Epilithon, leaf detritus, and seston (fine particulate organic matter in transport) were collected and analyzed for carbon (C), nitrogen (N), and phosphorus (P) content in an attempt to qualitatively assess the nutritional status of the diet of primary consumers. Macroinvertebrates were also analyzed for C, N, and P content to assess their nutritional composition in relation to their excretion and also to assess the nutritional composition of the diet of predatory insects and fish. Fish were also analyzed for C, N, and P.

Similar to theoretical predictions, fish and macroinvertebrate P excretion was negatively related to P content and the N:P excretion ratio was negatively related to the body N:P ratio. However, this relationship was driven primarily by two phosphorus rich species, mottled sculpin in the fish and crayfish in the macroinvertebrates. Some relationships did emerge between consumer excretion and diet. For example, hydropsychid caddisflies had the highest macroinvertebrate P excretion, possibly explained by the low N:P of seston. However, shredders, eating on a very low N and P diet of leaf detritus, had very low N and P excretion.

The relationship between consumers, their food, and nutrient excretion is a matter of mass balance. If the food N:P ratio is higher than that of the consumer, then the N:P excretion should be higher than the consumer N:P and the food N:P, especially if organisms are P-limited. However, N:P excretion by macroinvertebrates and fish were very similar despite large differences in diet. The majority of macroinvertebrates and fish had a lower N:P excretion ratio than the predicted N:P of their food, possibly indicating that 1) consumers were either selectively consuming more P-rich foods than the diets that I assigned them or 2) consumers are generally not N or P limited or influenced by the N or P in their diet. Mottled sculpin and crayfish were the only organisms with a higher N:P excretion than their resources and both had a higher %P than the other fish and macroinvertebrates, respectively. High N:P excretion along with high phosphorus content is indicative of P-limitation. Macroinvertebrates and fish, excluding mottled sculpin and crayfish, had a lower N:P excretion and the N:P ratio of the water column. If consumers do play a role in nutrient dynamics, then consumers could alter the relative abundance of nitrogen and phosphorus by supplying more phosphorus. However, the presence of a P-limited organism, such as mottled sclupin or crayfish, could alter the relative abundance of nitrogen and phosphorus by supplying less phosphorus.
Master of Science

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Vaillant, Grace C. „Nutrient cycling at cattle feedlots field & laboratory study“. Thesis, Manhattan, Kan. : Kansas State University, 2007. http://hdl.handle.net/2097/318.

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Oates, Richard Hunter. „Phosphate-mineral interactions and potential consequences for nutrient cycling“. Thesis, Online version of original thesis, 2008. http://hdl.handle.net/1912/2395.

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Mitchell, Mark E. „Nutrient Cycling Dynamics and Succession in Green Roof Ecosystems“. University of Cincinnati / OhioLINK, 2017. http://rave.ohiolink.edu/etdc/view?acc_num=ucin150487303109878.

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Bücher zum Thema "Nutrient cycling"

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Marschner, Petra, und Zdenko Rengel, Hrsg. Nutrient Cycling in Terrestrial Ecosystems. Berlin, Heidelberg: Springer Berlin Heidelberg, 2007. http://dx.doi.org/10.1007/978-3-540-68027-7.

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Petra, Marschner, und Rengel Zdenko, Hrsg. Nutrient cycling in terrestrial ecosystems. Berlin: Springer, 2007.

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Jorgensen, Jacques R. Foresters' primer in nutrient cycling. Asheville, N.C: U.S. Dept. of Agriculture, Forest Service, Southeastern Forest Experiment Station, 1986.

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Jorgensen, Jacques R. Foresters' primer in nutrient cycling. Asheville, N.C: U.S. Dept. of Agriculture, Forest Service, Southeastern Forest Experiment Station, 1986.

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G, Paoletti M., Foissner Wilhelm und Coleman David C. 1938-, Hrsg. Soil biota, nutrient cycling, and farming systems. Boca Raton: Lewis Publishers, 1993.

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Johnson, Dale W., und Steven E. Lindberg, Hrsg. Atmospheric Deposition and Forest Nutrient Cycling. New York, NY: Springer New York, 1992. http://dx.doi.org/10.1007/978-1-4612-2806-6.

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DeAngelis, D. L. Dynamics of Nutrient Cycling and Food Webs. Dordrecht: Springer Netherlands, 1992. http://dx.doi.org/10.1007/978-94-011-2342-6.

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Nilsson, L. O., R. F. Hüttl und U. T. Johansson, Hrsg. Nutrient Uptake and Cycling in Forest Ecosystems. Dordrecht: Springer Netherlands, 1995. http://dx.doi.org/10.1007/978-94-011-0455-5.

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Dynamics of nutrient cycling and food webs. London: Chapman & Hall, 1992.

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Nutrient cycling and limitation: Hawai'i as a model system. Princeton, NJ: Princeton University Press, 2004.

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Buchteile zum Thema "Nutrient cycling"

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Capinera, John L., Marjorie A. Hoy, Paul W. Paré, Mohamed A. Farag, John T. Trumble, Murray B. Isman, Byron J. Adams et al. „Nutrient Cycling“. In Encyclopedia of Entomology, 2646. Dordrecht: Springer Netherlands, 2008. http://dx.doi.org/10.1007/978-1-4020-6359-6_2275.

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Boyd, Claude E. „Nutrient Cycling“. In Aquaculture Pond Fertilization, 1–21. Oxford, UK: Wiley-Blackwell, 2012. http://dx.doi.org/10.1002/9781118329443.ch1.

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Chapin, F. Stuart, Pamela A. Matson und Peter M. Vitousek. „Nutrient Cycling“. In Principles of Terrestrial Ecosystem Ecology, 259–96. New York, NY: Springer New York, 2011. http://dx.doi.org/10.1007/978-1-4419-9504-9_9.

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Newell, Silvia E., Steven W. Wilhelm und Mark J. McCarthy. „Nutrient Cycling“. In Encyclopedia of Astrobiology, 1–7. Berlin, Heidelberg: Springer Berlin Heidelberg, 2019. http://dx.doi.org/10.1007/978-3-642-27833-4_5412-1.

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Newell, Silvia E., Steven W. Wilhelm und Mark J. McCarthy. „Nutrient Cycling“. In Encyclopedia of Astrobiology, 2124–30. Berlin, Heidelberg: Springer Berlin Heidelberg, 2023. http://dx.doi.org/10.1007/978-3-662-65093-6_5412.

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Eck, Mathilde, Oliver Körner und M. Haïssam Jijakli. „Nutrient Cycling in Aquaponics Systems“. In Aquaponics Food Production Systems, 231–46. Cham: Springer International Publishing, 2019. http://dx.doi.org/10.1007/978-3-030-15943-6_9.

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AbstractIn aquaponics, nutrients originate mainly from the fish feed and water inputs in the system. A substantial part of the feed is ingested by the fish and either used for growth and metabolism or excreted as soluble and solid faeces, while the rest of any uneaten feed decays in the tanks. While the soluble excretions are readily available for the plants, the solid faeces need to be mineralised by microorganisms in order for its nutrient content to be available for plant uptake. It is thus more challenging to control the available nutrient concentrations in aquaponics than in hydroponics. Furthermore, many factors, amongst others pH, temperature and light intensity, influence the nutrient availability and plant uptake. Until today, most studies have focused on the nitrogen and phosphorus cycles. However, to ensure good crop yields, it is necessary to provide the plants with sufficient levels of all key nutrients. It is therefore essential to better understand and control nutrient cycles in aquaponics.
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van Breemen, Nico. „Nutrient cycling strategies“. In Nutrient Uptake and Cycling in Forest Ecosystems, 321–26. Dordrecht: Springer Netherlands, 1995. http://dx.doi.org/10.1007/978-94-011-0455-5_37.

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Johnson, D. W., und G. S. Henderson. „Terrestrial Nutrient Cycling“. In Analysis of Biogeochemical Cycling Processes in Walker Branch Watershed, 233–300. New York, NY: Springer New York, 1989. http://dx.doi.org/10.1007/978-1-4612-3512-5_7.

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Escarré, Antoni, Ferran Rodà, Jaume Terradas und Xavier Mayor. „Nutrient Distribution and Cycling“. In Ecological Studies, 253–69. Berlin, Heidelberg: Springer Berlin Heidelberg, 1999. http://dx.doi.org/10.1007/978-3-642-58618-7_18.

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Everard, Mark. „Nutrient Cycling in Wetlands“. In The Wetland Book, 1–4. Dordrecht: Springer Netherlands, 2016. http://dx.doi.org/10.1007/978-94-007-6172-8_256-2.

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Konferenzberichte zum Thema "Nutrient cycling"

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Smith, Brett, Michael Kipp, Eva E. Stüeken und Roger Buick. „NUTRIENT CYCLING IN THE PHOSPHORIA SEA“. In GSA Annual Meeting in Seattle, Washington, USA - 2017. Geological Society of America, 2017. http://dx.doi.org/10.1130/abs/2017am-304043.

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Valek, Rachel Ann, Emily Sara Walmer, Cristian Alun Dorrett, Kaylee Brook Tanner, Anna Catherine Cardall, Gustavious Williams und Woodruff Miller. „Utah Lake Nutrient Cycling Studies: Limnocorral Usage and Experiments“. In 2022 Intermountain Engineering, Technology and Computing (IETC). IEEE, 2022. http://dx.doi.org/10.1109/ietc54973.2022.9796864.

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Singer, Jeremy W., Cynthia A. Cambardella und Thomas B. Moorman. „Coupling Manure Injection with Cover Crops to Enhance Nutrient Cycling“. In Proceedings of the 19th Annual Integrated Crop Management Conference. Iowa State University, Digital Press, 2007. http://dx.doi.org/10.31274/icm-180809-905.

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4

Dubeux, J. C. B., E. R. S. Santos, J. E. Portuguez-Acuna und L. M. D. Queiroz. „Nutrient Cycling and Crop Responses on Integrated Crop-Livestock Systems“. In XXV International Grassland Congress. Berea, KY 40403: International Grassland Congress 2023, 2023. http://dx.doi.org/10.52202/071171-0272.

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5

Wang, Xun, Xiangkun Zhu und Kan Zhang. „Biogeochemical Cycling of Nutrient Elements Following the Early Mesoproterozoic Oxygenation Event“. In Goldschmidt2020. Geochemical Society, 2020. http://dx.doi.org/10.46427/gold2020.2786.

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6

Meyer, Bryce L., und Nicholas S. Shepherd. „Nutrient Balance and Nitrogen Cycling In a Multistage, Multispecies Space Farm“. In AIAA SPACE 2016. Reston, Virginia: American Institute of Aeronautics and Astronautics, 2016. http://dx.doi.org/10.2514/6.2016-5586.

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7

Widga, Chris, Shawn Haugrud, Blaine Schubert, Steven C. Wallace, Brian Compton und Jim Mead. „MASTODONS, VERTEBRATE TAPHONOMY AND NUTRIENT CYCLING AT THE GRAY FOSSIL SITE“. In 67th Annual Southeastern GSA Section Meeting - 2018. Geological Society of America, 2018. http://dx.doi.org/10.1130/abs/2018se-311962.

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8

Burgess, Sarah A., Lee J. Florea, Tracy D. Branam und Meryem Ben Farhat. „CARBON AND NUTRIENT CYCLING IN SOUTH-CENTRAL INDIANA KARST: PRELIMINARY RESULTS“. In GSA Annual Meeting in Phoenix, Arizona, USA - 2019. Geological Society of America, 2019. http://dx.doi.org/10.1130/abs/2019am-339593.

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9

Ronnie W Schnell, Donald M Vietor, Richard H White, Clyde L Munster und Tony L Provin. „Cycling of Biosolids through Turfgrass Sod Prevents Sediment and Nutrient Loss“. In Watershed Management to Meet Water Quality Standards and TMDLS (Total Maximum Daily Load) Proceedings of the 10-14 March 2007, San Antonio, Texas. St. Joseph, MI: American Society of Agricultural and Biological Engineers, 2007. http://dx.doi.org/10.13031/2013.22463.

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10

Velho, Avantika, Pedro Cruz, David Banks-Richardson, Gabrielle Armin, Ying Zhang, Keisuke Inomura und Katia Zolotovsky. „Interactive Visualization of Plankton – Mediated Nutrient Cycling in the Narragansett Bay“. In OCEANS 2023 - MTS/IEEE U.S. Gulf Coast. IEEE, 2023. http://dx.doi.org/10.23919/oceans52994.2023.10337009.

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Berichte der Organisationen zum Thema "Nutrient cycling"

1

Peter A. Pryfogle. Nutrient Cycling Study. Office of Scientific and Technical Information (OSTI), September 2005. http://dx.doi.org/10.2172/966178.

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2

Coale, Kenneth H., und Kenneth S. Johnson. Trace Metal and Nutrient Cycling in San Francisco Bay. Fort Belvoir, VA: Defense Technical Information Center, September 1997. http://dx.doi.org/10.21236/ada629376.

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3

Jorgensen, Jacques R., und Carol G. Wells. A Loblolly Pine Management Guide: Foresters' Primer in Nutrient Cycling. Asheville, NC: U.S. Department of Agriculture, Forest Service, Southeastern Forest Experiment Station, 1986. http://dx.doi.org/10.2737/se-gtr-37.

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4

Sullivan, Matthew. Viruses in soils: Key modulators of microbiomes and nutrient cycling? (Final report). Office of Scientific and Technical Information (OSTI), September 2019. http://dx.doi.org/10.2172/2229275.

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5

McLaughlin, S. B., C. T. Garten und S. D. Wullschleger. Effects of acidic deposition on nutrient uptake, nutrient cycling and growth processes of vegetation in the spruce-fir ecosystem. Office of Scientific and Technical Information (OSTI), Oktober 1996. http://dx.doi.org/10.2172/451240.

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6

Fisher, Joshua, Richard Phillips und Tom Evans. Nutrient Cycle Impacts on Forest Ecosystem Carbon Cycling: Improved Prediction of Climate Feedbacks from Coupled C–Nutrient Dynamics from Ecosystem to Regional Scales. Office of Scientific and Technical Information (OSTI), August 2017. http://dx.doi.org/10.2172/1377633.

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7

Bravo, F., J. Grant und J. Barrell. Benthic habitat mapping and sediment nutrient cycling in a shallow coastal environment of Nova Scotia, Canada. Natural Resources Canada/ESS/Scientific and Technical Publishing Services, 2017. http://dx.doi.org/10.4095/305422.

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8

Finsterle, Stefan, Michael Kowalsky und Bhavna Arora. Developing an Automated Uncertainty Quantification Tool to Improve Watershed-Scale Predictions of Water and Nutrient Cycling. Office of Scientific and Technical Information (OSTI), August 2021. http://dx.doi.org/10.2172/1837753.

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9

Finsterle, Stefan, und Bhavna Arora. Developing an Automated Uncertainty Quantification Tool to Improve Watershed-Scale Predictions of Water and Nutrient Cycling. Office of Scientific and Technical Information (OSTI), April 2019. http://dx.doi.org/10.2172/1506118.

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10

Cseke, Leland. Nutrient cycling for biomass: Interactive proteomic/transcriptomic networks for global carbon management processes within poplar-mycorrhizal interactions. Office of Scientific and Technical Information (OSTI), August 2016. http://dx.doi.org/10.2172/1325004.

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