PMID- 15214631 OWN - NLM STAT- MEDLINE DCOM- 20041222 LR - 20131121 IS - 0723-2020 (Print) IS - 0723-2020 (Linking) VI - 27 IP - 3 DP - 2004 May TI - Nitrification and anammox with urea as the energy source. PG - 271-8 AB - Urea is present in many ecosystems and can be used as an energy source by chemolithotrophic aerobic ammonia oxidizing bacteria (AOB). Thus the utilization of urea in comparison to ammonia, by AOB as well as anaerobic ammonia oxidizing (Anammox) bacteria was investigated, using enrichments cultures, inoculated with activated sludge, and molecular ecological methods. In batch enrichment cultures grown with ammonia a population established in 2 weeks, which was dominated by halophilic and halotolerant AOB as determined by fluorescence in situ hybridization (FISH) experiments, with the 16S rRNA targeting oligonucleotide probe NEU. In other batch enrichment cultures using urea, the AOB population was assessed by PCR amplification, cloning and phylogenetic analysis of amoA and ribosomal 16S rRNA genes. While only one of the 48 16S rRNA gene clones could be identified as AOB (Nitrosomonas oligotropha), the amoA approach revealed two more AOB, Nitrosomonas europaea and Nitrosomonas nitrosa to be present in the enrichment. FISH analysis of the enrichment with probe NEU and newly designed probes for a specific detection of N. oligotropha and N. nitrosa related organisms, respectively, showed that N. oligotropha-like AOB formed about 50% of the total bacterial population. Also N. nitrosa (about 15% of the total population) and N. europaea (about 5% of the total population) were relatively abundant. Additionally, continuous enrichments were performed under oxygen limitation. When ammonia was the energy source, the community in this reactor consisted of Anammox bacteria and AOB hybridizing with probe NEU. As the substrate was changed to urea, AOB related to N. oligotropha became the dominant AOB in this oxygen limited consortium. This resulted in a direct conversion of urea to dinitrogen gas, without the addition of organic carbon. FAU - Sliekers, A Olav AU - Sliekers AO AD - Department of Biotechnology, Delft University of Technology, Delft, The Netherlands. FAU - Haaijer, Suzanne AU - Haaijer S FAU - Schmid, Markus AU - Schmid M FAU - Harhangi, Harry AU - Harhangi H FAU - Verwegen, Karin AU - Verwegen K FAU - Kuenen, J Gijs AU - Kuenen JG FAU - Jetten, Mike S M AU - Jetten MS LA - eng SI - GENBANK/AY343318 SI - GENBANK/AY343319 SI - GENBANK/AY343320 SI - GENBANK/AY343321 PT - Journal Article PT - Research Support, Non-U.S. Gov't PL - Germany TA - Syst Appl Microbiol JT - Systematic and applied microbiology JID - 8306133 RN - 0 (DNA, Bacterial) RN - 0 (DNA, Ribosomal) RN - 0 (RNA, Ribosomal, 16S) RN - 0 (Sewage) RN - 7664-41-7 (Ammonia) RN - 8W8T17847W (Urea) RN - N762921K75 (Nitrogen) SB - IM MH - Aerobiosis MH - Ammonia/*metabolism MH - Anaerobiosis MH - Bacteria, Anaerobic/*metabolism MH - DNA, Bacterial/chemistry/isolation & purification MH - DNA, Ribosomal/chemistry/isolation & purification MH - Ecosystem MH - Genes, Bacterial/genetics MH - Genes, rRNA/genetics MH - In Situ Hybridization, Fluorescence MH - Molecular Sequence Data MH - Nitrogen/metabolism MH - Nitrosomonas/classification/genetics/growth & development/*isolation & purification/*metabolism MH - Oxidation-Reduction MH - Phylogeny MH - RNA, Ribosomal, 16S/genetics MH - Sequence Analysis, DNA MH - Sequence Homology MH - Sewage/*microbiology MH - Urea/*metabolism EDAT- 2004/06/25 05:00 MHDA- 2004/12/23 09:00 CRDT- 2004/06/25 05:00 PHST- 2004/06/25 05:00 [pubmed] PHST- 2004/12/23 09:00 [medline] PHST- 2004/06/25 05:00 [entrez] AID - S0723-2020(04)70261-1 [pii] AID - 10.1078/0723-2020-00259 [doi] PST - ppublish SO - Syst Appl Microbiol. 2004 May;27(3):271-8. doi: 10.1078/0723-2020-00259.