Nitrate (
NO3
−) is highly water-soluble and considered to be the main nitrogen pollutants leached from agricultural soils. Its
presence in aquatic ecosystems is reported to cause various environmental and public health problems. Bioreactors containing
microbes capable of transforming NO3
− have been proposed as a means to remediate contaminated waters. Woodchip bioreactors
(WBRs) are continuous flow, reactor systems located below or above ground. Below ground systems are comprised
of a trench filled with woodchips, or other support matrices. The nitrate present in agricultural drainage wastewater passing
through the bioreactor is converted to harmless dinitrogen gas (
N2) via the action of several bacteria species. The WBR has
been suggested as one of the most cost-effective NO3
−-removing strategy among several edge-of-field practices, and has been
shown to successfully remove NO3
− in several field studies. NO3
− removal in the WBR primarily occurs via the activity of
denitrifying microorganisms via enzymatic reactions sequentially reducing NO3
− to N2.
While previous woodchip bioreactor
studies have focused extensively on its engineering and hydrological aspects, relatively fewer studies have dealt with the
microorganisms playing key roles in the technology. This review discusses NO3
− pollution cases originating from intensive
farming practices and N-cycling microbial metabolisms which is one biological solution to remove NO3
− from agricultural
wastewater. Moreover, here we review the current knowledge on the physicochemical and operational factors affecting
microbial metabolisms resulting in removal of NO3
− in WBR, and perspectives to enhance WBR performance in the future.
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The morphological switch from the yeast to hyphal form is a key virulence attribute of the opportunistic fungal pathogen,
Candida albicans. Our recent report showed that deletion of the newly identified apoptotic factor, CaNma111 or CaYbh3,
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