Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 1998 Aug;64(8):3042-51.
doi: 10.1128/AEM.64.8.3042-3051.1998.

Combined molecular and conventional analyses of nitrifying bacterium diversity in activated sludge: Nitrosococcus mobilis and Nitrospira-like bacteria as dominant populations

Affiliations

Combined molecular and conventional analyses of nitrifying bacterium diversity in activated sludge: Nitrosococcus mobilis and Nitrospira-like bacteria as dominant populations

S Juretschko et al. Appl Environ Microbiol. 1998 Aug.

Abstract

The ammonia-oxidizing and nitrite-oxidizing bacterial populations occurring in the nitrifying activated sludge of an industrial wastewater treatment plant receiving sewage with high ammonia concentrations were studied by use of a polyphasic approach. In situ hybridization with a set of hierarchical 16S rRNA-targeted probes for ammonia-oxidizing bacteria revealed the dominance of Nitrosococcus mobilis-like bacteria. The phylogenetic affiliation suggested by fluorescent in situ hybridization (FISH) was confirmed by isolation of N. mobilis as the numerically dominant ammonia oxidizer and subsequent comparative 16S rRNA gene (rDNA) sequence and DNA-DNA hybridization analyses. For molecular fine-scale analysis of the ammonia-oxidizing population, a partial stretch of the gene encoding the active-site polypeptide of ammonia monooxygenase (amoA) was amplified from total DNA extracted from ammonia oxidizer isolates and from activated sludge. However, comparative sequence analysis of 13 amoA clone sequences from activated sludge demonstrated that these sequences were highly similar to each other and to the corresponding amoA gene fragments of Nitrosomonas europaea Nm50 and the N. mobilis isolate. The unexpected high sequence similarity between the amoA gene fragments of the N. mobilis isolate and N. europaea indicates a possible lateral gene transfer event. Although a Nitrobacter strain was isolated, members of the nitrite-oxidizing genus Nitrobacter were not detectable in the activated sludge by in situ hybridization. Therefore, we used the rRNA approach to investigate the abundance of other well-known nitrite-oxidizing bacterial genera. Three different methods were used for DNA extraction from the activated sludge. For each DNA preparation, almost full-length genes encoding small-subunit rRNA were separately amplified and used to generate three 16S rDNA libraries. By comparative sequence analysis, 2 of 60 randomly selected clones could be assigned to the nitrite-oxidizing bacteria of the genus Nitrospira. Based on these clone sequences, a specific 16S rRNA-targeted probe was developed. FISH of the activated sludge with this probe demonstrated that Nitrospira-like bacteria were present in significant numbers (9% of the total bacterial counts) and frequently occurred in coaggregated microcolonies with N. mobilis.

PubMed Disclaimer

Figures

FIG. 1
FIG. 1
Phylogenetic tree showing the relationships of the Nitrospira-like organisms represented by 16S rDNA clones A-4 and A-11 from activated sludge, Nitrobacter isolate Nb4, and their closest relatives. The tree is based on the results of maximum-likelihood analysis. Together with a 16S rDNA clone retrieved from an SBR (GenBank accession no. X84560; 8), both clone sequences form a separate lineage within the nitrite-oxidizing bacteria of the Nitrospira group, which is also supported by maximum-parsimony and neighbor-joining analyses. Target organisms for probes S-*-Ntspa-1026-a-A-18 and NIT3 are indicated by brackets. Due to partial sequencing of the SBR clones (8), no information about their sequence in the target region of probe S-*-Ntspa-1026-a-A-18 is available. The bar represents 10% estimated sequence divergence.
FIG. 2
FIG. 2
In situ identification of nitrifying bacteria in activated sludge from the Kraftisried plant. (A) Simultaneous in situ hybridization with Cy3-labeled probe NmV and FLUOS-labeled probe NEU. N. mobilis cells appear yellow because of the overlapping labels. For visualization of the activated sludge floc, its autofluorescence was recorded with a 633-nm laser and colored blue by image analysis. (B) Simultaneous in situ identification of N. mobilis and Nitrospira-like bacteria after in situ hybridization with FLUOS-labeled probe NmV (green) and Cy3-labeled probe S-*-Ntspa-1026-a-A-18 (red). A phase-contrast image was superimposed for visualization of the floc material.
FIG. 3
FIG. 3
Phylogenetic tree showing the relationships of ammonia oxidizer isolates N. mobilis Nm93 and N. europaea Nm103 and their closest relatives among the beta subclass of Proteobacteria. The tree is based on the results of maximum-likelihood analysis. Target organisms for probes Nso190, Nso1225, Nsm156, Nsv443, NEU, S-*-Nse-1472-a-A-18, and NmV are indicated by brackets. The bar represents 10% estimated sequence divergence.
FIG. 4
FIG. 4
Direct and nested PCR amplification of an amoA fragment from N. europaea Nm50 and from activated sludge (Kraftisried). Direct PCR amplification was performed with primers AMO-F and AMO-R (lanes 2, 4, 6, 8, and 10), and nested PCR amplification was performed with primers AMO-F and AMO-R, followed by primers AMO-F2 and AMO-R2 (lanes 3, 5, 7, 9, and 11). Lanes: 1 and 12, 1-kb DNA ladder; 2 and 3, water control; 4 and 5, 25 ng of N. europaea DNA; 6 and 7, 25 ng of activated sludge DNA; 8 and 9, 50 ng of activated sludge DNA; 10 and 11, 100 ng of activated sludge DNA.
FIG. 5
FIG. 5
Maximum-likelihood tree based on partial amoA gene sequences showing the phylogenetic positions of the amoA gene stretches from ammonia oxidizer isolates N. mobilis Nm93 and N. europaea Nm103 and the environmental sequences retrieved from activated sludge. The bar indicates 10% estimated sequence divergence.

Similar articles

Cited by

References

    1. Alm E, Oerther D B, Larsen N, Stahl D A, Raskin L. The oligonucleotide probe database. Appl Environ Microbiol. 1996;62:3557–3559. - PMC - PubMed
    1. Amann R I. In situ identification of micro-organisms by whole cell hybridization with rRNA-targeted nucleic acid probes. In: Akkerman A D C, van Elsas J D, de Bruijn F J, editors. Molecular microbial ecology manual. Dordrecht, The Netherlands: Kluwer Academic Publishers; 1995. pp. 1–15.
    1. Arthur J W, West C W, Allen K N, Hedke S F. Seasonal toxicity of ammonia to five fish and nine invertebrate species. Bull Environ Contam Toxicol. 1987;38:324–331. - PubMed
    1. Belser L W. Population ecology of nitrifying bacteria. Annu Rev Microbiol. 1979;3:309–333. - PubMed
    1. Bock E, Sundermayer-Klinger H, Stackebrandt E. New facultative lithotrophic nitrite-oxidizing bacteria. Arch Microbiol. 1983;136:281–284.

Publication types

MeSH terms

LinkOut - more resources

-