An oxygen minimum zone (OMZ) is characterized as an oxygen-deficient layer in the world's oceans. Typically found between 200 m to 1500 m deep below regions of high productivity, such as the western coasts of continents. OMZs can be seasonal following the spring-summer upwelling season. Upwelling of nutrient-rich water leads to high productivity and labile organic matter, that is respired by heterotrophs as it sinks down the water column. High respiration rates deplete the oxygen in the water column to concentrations of 2 mg/L or less forming the OMZ. OMZs are expanding, with increasing ocean deoxygenation. Under these oxygen-starved conditions, energy is diverted from higher trophic levels to microbial communities that have evolved to use other biogeochemical species instead of oxygen, these species include nitrate, nitrite, sulphate etc. Several Bacteria and Archea have adapted to live in these environments by using these alternate chemical species and thrive. The most abundant phyla in OMZs are Pseudomonadota, Bacteroidota, Actinomycetota, and Planctomycetota. In the absence of oxygen, microbes use other chemical species to carry out respiration, in the order of the electrochemical series. With nitrate and nitrite reduction yielding as much energy as oxygen respiration, followed by manganese and iodate respiration and yielding the least amount of energy at the bottom of the series are the iron and sulfate reducers. The utilization of these chemical species by microbes plays an important role in their biogeochemical cycling in the world's oceans.
Life in anoxic conditions
Nitrogen cycling Biological productivity (photosynthesis) in marine ecosystems is often limited by the bioavailability of nitrogen. The amount of bioavailable nitrogen (nitrate (NO3−), nitrite (NO2−), and ammonium (NH4+)) depends on the inputs from nitrogen fixation and losses from denitrification and anammox as dinitrogen gas (N2), a compound only accessible to nitrogen-fixing bacteria. N2 production from denitrification and anammox closes the nitrogen cycle by reducing the nitrogen available in organic matter fixed by phytoplankton at the surface ocean. Denitrification in OMZs leads to a significant loss of inorganic nitrogen from the oceans, limiting growth/productivity in many regions worldwide. OMZs play a key role in the global nitrogen cycle. As no oxygen is present to fuel aerobic respiration, anoxic systems are primarily dominated by microbially-mediated nitrogen cycling. N2 fixation is performed by diazotrophs (N2 fixing bacteria and archaea), which convert N2 gas into ammonia (NH3). The amount of N2 fixation and the distribution of diazotrophs in the ocean is determined by the availability of oxygen (O2), light, phosphorus (P), iron (Fe), and organic matter, as well as habitat temperature. N2 fixation has been found in some anoxic systems, generally associated with sulfate reducers or oxidizers. However, heterotrophic denitrification is a more dominant process under anoxic conditions. Denitrification is the reduction of NO3− and NO2− to the gaseous form of nitrogen (N2), including the greenhouse gas nitrous oxide (N2O). Heterotrophic denitrification is a multi-step process that uses organic matter to reduce NO3− to N2 in oxygen-depleted environments like OMZs and sediments. In OMZs, different steps in the denitrification processes are performed by separate groups of bacteria, and these denitrifiers are often found directly on sinking organic matter particles, which are hotspots of microbial activity. The first step of denitrification is nitrate reduction where NO3− is reduced to NO2− by the protein nitrate reductase. Anaerobic ammonia-oxidizing bacteria (anammox) convert NO2− and NH4+ to N2 using an enzyme called hydrazine oxidoreductase. Genomic studies conducted in these ecosystems reveal a growing abundance of genes encoding proteins responsible for dissimilatory nitrate reduction to ammonium (DNRA) and anammox at the core of these OMZs. Such studies provide information to map out the nitrogen cycle and demystify missing links and unexplored pathways in the water column. Anammox is often coupled to denitrification as a source of NH4+ in OMZs or to DNRA in sediments. DNRA has been found to be the dominant process supplying NH4+ near the shelf and upper slope of sediments because of the presence of large bacterial mats made up of the giant sulfur-oxidizing bacteria Thioploca spp. and Beggiatoa spp. which reduce NO3− and/or NO2− to NH4+ using reduced sulfur. Denitrification and anammox account for about 30-50% of the N-losses in OMZs, where the total N-loss is determined by the supply of sinking organic matter available. Additionally, ammonium and nitrite oxidation are key processes in N cycling in anoxic environments. Ammonium oxidation is the first step in nitrification and ammonia-oxidizing bacteria (AOB) converts NH3 to NO2−. Followed by nitrite oxidation by nitrite-oxidizing bacteria (NOB), which converts NO2− to NO3−. Ammonium and nitrite oxidizers have a high affinity for O2 and can use nanomolar concentrations of O2 to oxidize ammonium and nitrite. These small concentrations of O2 can be supplied by photosynthesis by Prochlorococcus spp. or by horizontal mixing by jets and eddies. In anoxic environments, the competition between ammonium and nitrite oxidization and anammox and denitrification for ammonium and nitrite play an important role in controlling nitrogen loss in OMZs.
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