Book Chapter10.1016/BS.AAMBS.2018.10.003
Nitrogen cycling during wastewater treatment.
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TL;DR: A number of promising new biological treatment technologies are emerging and it is hoped that as the cost of these practices goes down more wastewater treatment plants will start to include a tertiary treatment step.
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Abstract: Many wastewater treatment plants in the world do not remove reactive nitrogen from wastewater prior to release into the environment. Excess reactive nitrogen not only has a negative impact on human health, it also contributes to air and water pollution, and can cause complex ecosystems to collapse. In order to avoid the deleterious effects of excess reactive nitrogen in the environment, tertiary wastewater treatment practices that ensure the removal of reactive nitrogen species need to be implemented. Many wastewater treatment facilities rely on chemicals for tertiary treatment, however, biological nitrogen removal practices are much more environmentally friendly and cost effective. Therefore, interest in biological treatment is increasing. Biological approaches take advantage of specific groups of microorganisms involved in nitrogen cycling to remove reactive nitrogen from reactor systems by converting ammonia to nitrogen gas. Organisms known to be involved in this process include autotrophic ammonia-oxidizing bacteria, heterotrophic ammonia-oxidizing bacteria, ammonia-oxidizing archaea, anaerobic ammonia oxidizing bacteria (anammox), nitrite-oxidizing bacteria, complete ammonia oxidizers, and dissimilatory nitrate reducing microorganisms. For example, in nitrifying-denitrifying reactors, ammonia- and nitrite-oxidizing bacteria convert ammonia to nitrate and then denitrifying microorganisms reduce nitrate to nonreactive dinitrogen gas. Other nitrogen removal systems (anammox reactors) take advantage of anammox bacteria to convert ammonia to nitrogen gas using NO as an oxidant. A number of promising new biological treatment technologies are emerging and it is hoped that as the cost of these practices goes down more wastewater treatment plants will start to include a tertiary treatment step.
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References
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TL;DR: A continuous-upflow biofilter packed with sponge iron was constructed for nitrate removal under an anaerobic atmosphere and the maximum nitrogen removal efficiency was about 90 % with Fe(II)EDTA level of 1100 mg/L.
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Aquarium nitrification revisited: Thaumarchaeota are the dominant ammonia oxidizers in freshwater aquarium biofilters
Laura A. Sauder,Katja Engel,Jennifer C. Stearns,Andre P. Masella,Richard Pawliszyn,Josh D. Neufeld +5 more
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Interactions between N application rate, CH4 oxidation and N2O production in soil
Stuart Acton,Elizabeth M. Baggs +1 more
TL;DR: In this article, a controlled environment experiment was conducted to quantify methane oxidation rates and source partition N2O production in a silt loam soil following application of NH4NO3.
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Vertical activity distribution of dissimilatory nitrate reduction in coastal marine sediments
TL;DR: The relative importance of denitrification and dissim- ilatory nitrate reduction to ammonium (DNRA) was investigated in intact sediment cores from five different coastal marine field sites (Dorum, Aarhus Bight, Mississippi Delta, Limfjord and Janssand) as mentioned in this paper.
Diversity, abundance and activity of ammonia-oxidizing microorganisms in fine particulate matter
TL;DR: An important role of AOA and Comammox in ammonia oxidation in PM2.5 is pointed towards and the diversity, abundance and activity of ammonia oxidizer archaea, ammonia oxidizing bacteria and complete ammonia oxidizers in Beijing-Tianjin-Hebei megalopolis, China was investigated.