Skip to main content

Design and evaluation of 16S rRNA sequence based oligonucleotide probes for the detection and quantification of Comamonas testosteroni in mixed microbial communities



The β-proteobacterial species Comamonas testosteroni is capable of biotransformation and also biodegradation of a range of chemical compounds and thus potentially useful in chemical manufacturing and bioremediation. The ability to detect and quantify members of this species in mixed microbial communities thus may be desirable.


We have designed an oligonucleotide probe for use in fluorescent in situ hybridization (FISH) and two pairs of PCR primers targeting a C. testosteroni subgroup. The FISH probe and one of the PCR primer pairs are suitable for quantification of C. testosteroni in mixed microbial communities using FISH followed by quantitative image analysis or real-time quantitative PCR, respectively. This has been shown by analysis of samples from an enrichment of activated sludge on testosterone resulting in an increase in abundance and finally isolation of C. testosteroni. Additionally, we have successfully used quantitative PCR to follow the C. testosteroni abundance during a laboratory scale wastewater bioaugmentation experiment.


The oligonucleotides presented here provide a useful tool to study C. testosteroni population dynamics in mixed microbial communities.


Comamonas testosteroni is a ubiquitously occuring β-proteobacterial species which has been isolated from aquatic as well as terrestrial environments. It has been shown to be capable of transformations of steroid compounds [14] and also of degradation of aromatic hydrocarbons [510]. C. testosteroni is thus of interest for potential biotechnological applications such as chemical transformations in fine chemical manufacturing [11] and bioremediation processes [7, 12], as indicated by laboratory results.

Due to the widespread environmental distribution and the potential relevance of C. testosteroni in biotransformation processes, it may be of interest to follow the population dynamics of this species over time in a mixed-species environment. Since culture-dependent methods are not sufficiently accurate to detect and quantify one particular species within a mixed bacterial community, methods targeting the 16S rRNA and/or its gene(s) need to be applied to such a problem, as has already been done in previous investigations [1316]. Probes for species of the genera Comamonas and Delftia (COM1424 [17], and PPT [18]) as well as for species of the family Comamonadaceae (CTE [19]) have been described earlier, but might lack the desired specificity. The use of reporter genes such as gfp or dsRed is also possible, but only applicable to environments with intentionally introduced labelled strains and not to the investigation of uncharacterized environmental samples. Additionally, the introduction of reporter genes may impair the environmental fitness of the introduced strain [20], and variations in reporter expression might interfere with detection. The use of reporter gene carrying strains also means working with genetically modified organisms, which may not be possible in all cases.

The following study reports on the development of 16S rRNA sequence based oligonucleotide probes which are suitable for detection and quantification of Comamonas testosteroni in mixed cultures using PCR and/or fluorescent in situ hybridization (FISH).


16S rRNA sequence diversity of Comamonas testosteroni

A short survey of 16S rRNA sequence diversity of C. testosteroni was carried out. Fig. 1 shows a phylogenetic tree based on 16S rRNA sequences of species of the genera Comamonas and Delftia, with an emphasis on sequences of C. testosteroni isolates with more than 1200 bp length available from Ribosomal Database Project II. The C. testosteroni sequences form two clades (designated A and B) with a sequence divergence of approximately 1%. Clade A contains far more sequences than clade B, and all physiologically characterized strains as well as all strains isolated during studies dealing with biotransformation or biodegradation fall within this clade.

Figure 1

Neighbour-joining tree of 16S rRNA gene sequences of species of the genera Comamonas and Delftia with an emphasis on Comamonas testosteroni corresponding to E. coli positions 135-1369. The sequences of Ideonella dechloratans CCUG 30898T [GenBank:X72724] and of Rubrivivax gelatinosus ATCC 17011T [GenBank:D16213] were used as outgroups. Bootstrap values of 1000 resamplings are shown at the branch points.

Probe design

The sequence alignment from which the tree was constructed was then used as a basis to identify sequence regions which could be used for the design of FISH probes and PCR primers specific for C. testosteroni. Useful stretches were identified around nucleotides 450–480, 990–1020, and 1130–1160 (E. coli numbering). However, it was not possible to design oligonucleotides targeting simultaneously sequences from clades A and B together. Since clade A seemed to contain the organisms with a higher environmental and biotechnological relevance, we decided to design probes targeting this sequence cluster. Two PCR primer pairs and one FISH probe were designed (see Table 1). BLAST searches revealed that these oligonucleotides had a complete match only with sequences showing >99% identity to the sequence of the C. testosteroni type strain.

Table 1 PCR primers and FISH probes used in this study

Pure culture evaluation of the designed oligonucleotides

All oligonucleotides were evaluated in situ on a selection of proteobacterial pure cultures including all C. testosteroni strains available from the German Collection of Microorganisms (DSM). The tests revealed that the newly designed primers and probe were specific for the strains of this species. Primer pair CteA1 yielded a PCR product with a size of 571 bp, whereas primer pair CteA2 produced an amplicon of 167 bp length. It should be noted here that both primer pairs produced products from all examined C. testosteroni cultures, indicating that all tested cultures fell within clade A. A clade B culture was not available for testing, but since all developed oligonucleotides except primer CteA2-rev show 3 or more mismatches with the available clade B sequences, it can be expected that these strains would be excluded from detection by PCR or FISH. The CY3 labelled FISH probe CteA gave well-fluorescing signals when used with 30% of formamide in the hybridization buffer. Cells of all available C. testosteroni isolates except of strain DSM 6781 gave well-fluorescing signals when FISH was applied to paraformaldehyde fixed cells. To identify the reason for the reduced signal intensity in strain DSM 6781, its 16S rRNA sequence was determined [EMBL:AM113745]. The sequence had a central mismatch with probe CteA. Accordingly, we suggest to work with a degenerate version of the probe with the sequence CAT GAC CCG (G/A)GG ATA TTA GC. All non-target strains tested did not produce PCR products with primers CteA1 and CteA2, nor did they give a fluorescence signal when using probe CteA in FISH, although low background fluorescence was observed in some cultures.

Analysis of testosterone enrichment cultures and isolates

In order to test the developed oligonucleotides on an unknown mixed culture, we provided conditions for the enrichment of C. testosteroni from activated sludge by two successive enrichment steps in liquid media containing testosterone as the sole source of carbon and energy and finally by spreading samples of the second culture on agar plates composed of the same medium. Samples of the activated sludge, the two enrichment cultures, and of five isolates obtained from the testosterone plates were then analysed by PCR and FISH.

Fig. 2 shows the results of an end-point PCR reaction (30 cycles) carried out using primer pair CteA1. No product was obtained from DNA from the activated sludge, suggesting a low initial abundance of C. testosteroni. In contrast, DNA samples from both enrichment cultures as well as two of the isolates produced a band at 570 bp, indicating a successful enrichment and isolation of C. testosteroni. When the PCR product amplified from the first enrichment culture was subjected to direct sequencing, a clean sequence [EMBL:AM113744] with 461 of the 462 obtained nucleotides identical to the sequence of C. testosteroni DSM 50244 was retrieved. Partial analysis of the 16S sequences of the isolates [EMBL:AM113739–AM113743] showed that the two isolates giving PCR products with the CteA1 primers displayed 100% sequence identity with the sequence of C. testosteroni DSM 50244, whereas the other isolates showed 100% identities to the sequences of Pseudomonas sp. B13 [GenBank:AF039489], Pseudomonas sp. WAS2 [GenBank:AB007999], and Rhodococcus equi [GenBank:AF490539], respectively. The two C. testosteroni strains could also be identified by FISH using the probe CteA.

Figure 2

Agarose gel showing PCR products obtained using the primer pair CteA1 from the testosterone enrichment cultures and the isolates grown on testosterone plates. M: 100 bp ladder, +ve: positive control (C. testosteroni genomic DNA), AS: activated sludge inoculum, E1: first enrichment step, E2: second enrichment step, I1–I5: isolates, -ve: negative control (no template DNA).

In order to assess the suitability of the oligonucleotides for quantification of C. testosteroni in mixed cultures, primer pair CteA2 was used in real-time quantitative PCR and probe CteA was used for quantitative image analysis. The primer pair Eub341F/534R and the FISH probes Eub338 mix were used in parallel as a measure of total cell abundance. The ratios between C. testosteroni specific signals and the eubacterial specific signals will produce a fractional number representing the C. testosteroni abundance in a given sample. This approach has been applied to cells labelled by FISH [21] or fluorescent proteins [22] and has also been used in real-time PCR quantification [14].

A dilution series of genomic DNA of C. testosteroni DSM 50244 yielded products from 5 fg on, which can be considered the detection limit, and showed a linear relationship between the Ct-value and the log(DNA amount) over 5 orders of magnitude (50 fg to 0.5 ng, Fig. 3a) with nearly identical slopes close to the optimal value of -3.32 for the CteA2 and the Eub primer pairs. This indicates that both primer pairs are suitable for use in qPCR analysis. A comparison of the C. testosteroni fractional numbers obtained by qPCR and FISH (Fig. 3b) shows identical trends for the abundances of C. testosteroni in the activated sludge and the following two enrichment steps. The initial C. testosteroni abundance was low (0.003% by qPCR, not detectable by FISH), and increased via a moderate level in the first enrichment culture (3% by qPCR and FISH) to a major proportion of the population detected by the EUB primers or probe mix (50% by qPCR and 70% by FISH) in the second enrichment culture.

Figure 3

a) Real-time PCR standard curves obtained using primer pairs CteA2 (Cte, diamonds) and 341F/534R (Eub, squares) using 10fold serial dilutions of C. testosteroni genomic DNA as template DNA. Linear regressions are calculated using the large dots of each series. Error margins are too small to be visible. b) Abundances of C. testosteroni in the activated sludge inoculum (AS) and the two testosterone enrichment steps (E1 and E2) as measured by real-time PCR and quantitative FISH. nd: not detectable.

Determination of C. testosteroni abundance in a reactor bioaugmentation experiment via quantitative PCR

A further test of the qPCR primers CteA2 in mixed culture experiments was done on DNA samples extracted from 3 laboratory scale biofilm reactors in an experiment to introduce degradation of 3-chloroaniline (3CA) via conjugal transfer of the 3CA-degradative plasmid pNB2. A full description of the experiment can be found elsewhere [23]. Briefly, all reactors where initially inoculated with an activated sludge-derived mixed bacterial culture. Reactor PB then received a Pseudomonas putida strain and reactor P received a Comamonas testosteroni strain, both carrying plasmid pNB2, whereas control reactor N did not receive additional bacteria. The P. putida strain was not able to degrade 3CA, whereas the C. testosteroni strain was. All reactors received a feed containing 3CA and four easily degradable carbon sources (glucose, gluconate, acetate, citrate). Reactor PB started to degrade 3CA after an initial lag phase, and finally, a number of C. testosteroni pNB2-transconjugants capable of 3CA-degradation could be isolated from this reactor. Reactor P showed 3CA-degradation from the beginning of the experiment on, whereas no degradation could be observed in reactor N.

Using quantitative PCR, we determined the C. testosteroni abundance in DNA samples obtained at the start of the experiment (day 0) as well as on day 18 after onset of degradation of reactor P and towards the end of the experiment on day 29 (Fig. 4). Whereas initial abundance of C. testosteroni in reactor PB was low around 1% and rose via 3% to a final level of 9%, reactor P initially showed a high C. testosteroni abundance of 36% due to addition of the pNB2-carrying C. testosteroni strain which then dropped to values around 18%. Surprisingly, reactor N showed the same trend as reactor PB with an increase of the C. testosteroni abundance from low levels of 2% to finally 10%. Although the increase in C. testosteroni abundance in reactor PB is partly explained by growth of a 3CA-degrading, pNB2-carrying C. testosteroni subpopulation, this indicates that also non-degrading C. testosteroni strains might benefit from the general growth conditions in our reactors.

Figure 4

Abundances of C. testosteroni during a bioaugmentation experiment [23] using laboratory scale biofilm reactors inoculated with activated sludge bacteria. Reactors PB and P additionally received a P. putida and a C. testosteroni strain, respectively.


In our study, we present two sets of PCR primers and an rRNA directed oligonucleotide probe for use in FISH which can be applied for detection and quantification of a Comamonas testosteroni subgroup in mixed bacterial populations.

Relative quantifications (target group vs. a measure of whole eubacterial cell abundance) conducted by real-time PCR and FISH followed by image analysis demonstrate the same development of C. testosteroni populations during an enrichment process using testosterone as a carbon source. However, since neither of the two methods measure cell number, but rRNA gene copy number (PCR) and cell area (FISH), a direct numerical comparison is not possible here. Both quantification methods may display a sample-inherent bias, when the average 16S rRNA gene copy number per cell differs from the number of 16S rRNA gene copies per C. testosteroni cell in PCR or the average cell area in a sample differs from the average area of a C. testosteroni cell in FISH. Additionally, we applied the real-time PCR approach presented here to successfully determine abundance of C. testosteroni in a set of laboratory-scale wastewater treatment reactors inoculated with activated sludge bacteria and additionally bioaugmented with different bacteria of which one was a C. testosteroni strain.

Comparison of the target groups of the new probe set with the previously described probes targeting Comamonas species reveals that our oligonucleotides exclusively match sequences of Comamonas testosteroni strains. Primer CteA2-rev is somewhat less specific, but the combination with primer CteA2-for ensures specificity of the primer pair. In contrast, probe CTE matches with most sequences of the genera Comamonas, Acidovorax and Hydrogenophaga, but has mismatches with the sequences of C. koreensis, Comamonas sp. 12022, C. testosteroni SMCC B329 (clade B), and of the Delftia species among the sequences shown in Fig. 1. Probe PPT targets mainly Comamonas and Acidovorax, but both PPT and CTE also target a range of sequences from other genera of the Comamonadaceae [24]. Among the previously published probes, COM1424 has the narrowest range targeting predominantly Comamonas and Delftia [24].


The oligonucleotides presented here are a useful tool to study C. testosteroni population dynamics in mixed microbial communities, when considering the method-inherent bias disussed above.


Bacterial strains and culture conditions

The following strains of Comamonas testosteroni were used: DSM 38, 1455, 1622, 6781, 11414, 12678, 50241, 50242, 50244, LMG 19554, SB3 [25] and SB4 [25]. In addition, C. aquatica ATCC 11330, C. nitrativorans DSM 13191, C. koreensis TK17 [26], C. terrigena TK41 [26], Delftia acidovorans ATCC 15668, Delftia tsuruhatensis SB5 [25], Pseudomonas putida DSM 291, Pseudomonas aeruginosa PAO1 [27], Novosphingobium capsulatum DSM 30196, Aeromonas hydrophila DSM 30187, Escherichia coli DH5α, Serratia ficaria ATCC 33105, Acinetobacter calcoaceticus BD413 [28], Ralstonia eutropha DSM 531, and Burkholderia cepacia H111 [29] were included as non-target organisms. All cultures were maintained on nutrient broth at 30°C.

Enrichment of Comamonas testosteroni from activated sludge

Activated sludge was obtained from the aeration basin of the municipal wastewater treatment plant Garching (Germany). A sample representing approximately 1 mg of dry weight was inoculated into 25 ml of MMO medium [30] containing 0.05% testosterone (added as a 10% solution in DMSO) as the sole carbon source and incubated for 4 d (30°C, 150 rpm), until the disappearance of the testosterone crystals indicated degradation of the compound. 250 μl of this culture was inoculated into 25 ml of fresh medium and again incubated for 2 d, and a sample was spread onto MMO plates with testosterone which were incubated for 7 d at 30°C.

Primer and probe design and evaluation

A multiple sequence alignment and calculation of a phylogenetic tree of a selection of 16S rRNA gene sequences of the genus Comamonas was done using ClustalX 1.81 [31] (see Fig. 1 for the sequences included in the analysis). Sequence stretches showing identities within C. testosteroni clade A sequences, but having mismatches to the remaining sequences, were used to design species-specific oligonucleotides. The sequences of the oligonucleotides which were finally used in this study are shown in Table 1.

The specificities of the primers and probes developed in this study as well as those of the probes COM1424, CTE, and PPT were checked using BLAST within the NCBI website [32] as well as the ProbeMatch tool in the RDP-II [33].


For PCR from pure cultures, cells suspended in water were used as template DNA. DNA from activated sludge and the enrichment cultures was isolated as described previously [34].

Conventional PCR was carried out using a Mastercycler gradient (Eppendorf, Hamburg, Germany) and Qiagen HotStarTay DNA Polymerase (Qiagen, Hilden, Germany). A single reaction contained 0.2 μM of each primer CteA1-for and CteA1-rev, 0.2 mM of each dNTP, 1.5 mM MgCl2, 0.02 U/μl of Taq Polymerase in a volume of 20 μl. Either 1 μl of cell suspension or 10 ng of DNA was added as template DNA. The PCR protocol consisted of an initial denaturation of 15 min at 95°C followed by 30 cycles of 30 sec at 95°C, 1 min at 58°C and 2 min at 72°C and was concluded by a final extension of 8 min at 72°C. To exclude the possibility of PCR inhibition, parallel positive control reactions using the general eubacterial primers 341F and 534R were conducted for each template. The 16S rRNA genes of isolates were partially amplified using primers 27F and 1492R [35] and custom sequenced using primer 341F by MWG Biotech (Ebersberg, Germany). PCR products were analysed on 2% TAE agarose gels.

Real-time PCR was carried out in an ABI GeneAmp 5700 device (Applied Biosystems, Foster City, USA) using the Qiagen Quantitect SYBR Green PCR Kit. Each reaction was performed in triplicate and contained 12.5 μl of PCR-Mastermix, 0.2 μM of either each primer CteA2-for and CteA2-rev or 341f and 534r, 5 mM MgCl2, and 5 μl of template DNA in a final volume of 25 μl. The thermal protocol consisted of 15 min at 95°C followed by 40 cycles of 15 sec at 95°C and 60 sec at 60°C. The same serial 10fold dilutions of genomic DNA of Comamonas testosteroni DSM 50244T were used to generate standard curves for both primer pairs.

FISH and image analysis

FISH was performed as described [36], using paraformaldehyde as a fixative. For elucidation of the hybridization conditions for the probe CteA, hybridization temperature was kept constant at 46°C. The formamide concentration in the hybridization buffer was varied by 10% increments. C. testosteroni LMG 19554 and C. aquatica ATCC 11330 were used as positive and negative controls, respectively. The formamide concentration which resulted in clear strong signals for C. testosteroni and no signals for C. aquatica was used in subsequent hybridizations. Probe CteA was labelled with the cyanine dye CY3, whereas the EUB probe mix (an equimolar mixture of probes EUB338, EUB338-II, and EUB338-III) was labelled with the cyanine dye CY5. All hybridizations were performed as simultaneous dual colour hybridizations where the EUB mix served the role of a general counter stain for total bacterial cell number. Images were recorded using a Zeiss LSM 510 Meta (Carl Zeiss, Jena, Germany) confocal laser scanning microscope. For quantitative analyses, the percentages of area coverage of signals from the CteA probe and the EUB mix were calculated using the Quantimet Q500W (Leica, Cambridge, England) image analysis system. The abundance of C. testosteroni was calculated as the ratio of the area covered by biomass stained simultaneously with both CteA and EUB probes to the area covered by EUB-stained biomass only. For each sample, 20 microscopic fields (92 × 92 μm) were analysed.

Accession numbers

The 16S rRNA sequences determined in this study have been deposited in the EMBL nucleotide sequence database [37] under the accession numbers [EMBL:AM113739–AM113745].


  1. 1.

    Horinouchi M, Kurita T, Yamamoto T, Hatori E, Hayashi T, Kudo T: Steroid degradation gene cluster of Comamonas testosteroni consisting of 18 putative genes from meta-cleavage enzyme gene tesB to regulator gene tesR. Biochem Biophys Res Commun. 2004, 324 (2): 597-604. 10.1016/j.bbrc.2004.09.096.

    CAS  Article  PubMed  Google Scholar 

  2. 2.

    Horinouchi M, Hayashi T, Yamamoto T, Kudo T: A new bacterial steroid degradation gene cluster in Comamonas testosteroni TA441 which consists of aromatic-compound degradation genes for seco-steroids and 3-ketosteroid dehydrogenase genes. Appl Environ Microbiol. 2003, 69 (8): 4421-4430. 10.1128/AEM.69.8.4421-4430.2003.

    PubMed Central  CAS  Article  PubMed  Google Scholar 

  3. 3.

    Skowasch D, Mobus E, Maser E: Identification of a novel Comamonas testosteroni gene encoding a steroid-inducible extradiol dioxygenase. Biochem Biophys Res Commun. 2002, 294 (3): 560-566. 10.1016/S0006-291X(02)00516-8.

    CAS  Article  PubMed  Google Scholar 

  4. 4.

    Oppermann UC, Maser E: Characterization of a 3 alpha-hydroxysteroid dehydrogenase/carbonyl reductase from the gram-negative bacterium Comamonas testosteroni. Eur J Biochem. 1996, 241 (3): 744-749. 10.1111/j.1432-1033.1996.00744.x.

    CAS  Article  PubMed  Google Scholar 

  5. 5.

    Sondossi M, Barriault D, Sylvestre M: Metabolism of 2,2'- and 3,3'-dihydroxybiphenyl by the biphenyl catabolic pathway of Comamonas testosteroni B-356. Appl Environ Microbiol. 2004, 70 (1): 174-181. 10.1128/AEM.70.1.174-181.2004.

    PubMed Central  CAS  Article  PubMed  Google Scholar 

  6. 6.

    Chen F, Cui M, Fu J, Sheng G, Sun G, Xu M: Biodegradation of quinoline by freely suspended and immobilized cells of Comamonas sp strain Q10. J Gen Appl Microbiol. 2003, 49 (2): 123-128. 10.2323/jgam.49.123.

    CAS  Article  PubMed  Google Scholar 

  7. 7.

    Boon N, Goris J, De Vos P, Verstraete W, Top EM: Bioaugmentation of activated sludge by an indigenous 3-chloroaniline-degrading Comamonas testosteroni strain, I2gfp. Appl Environ Microbiol. 2000, 66 (7): 2906-2913. 10.1128/AEM.66.7.2906-2913.2000.

    PubMed Central  CAS  Article  PubMed  Google Scholar 

  8. 8.

    Junker F, Saller E, Schlafli Oppenberg HR, Kroneck PM, Leisinger T, Cook AM: Degradative pathways for p-toluenecarboxylate and p-toluenesulfonate and their multicomponent oxygenases in Comamonas testosteroni strains PSB-4 and T-2. Microbiology. 1996, 142: 2419-2427.

    CAS  Article  PubMed  Google Scholar 

  9. 9.

    Goyal AK, Zylstra GJ: Molecular cloning of novel genes for polycyclic aromatic hydrocarbon degradation from Comamonas testosteroni GZ39. Appl Environ Microbiol. 1996, 62 (1): 230-236.

    PubMed Central  CAS  PubMed  Google Scholar 

  10. 10.

    Wang YZ, Zhou Y, Zylstra GJ: Molecular analysis of isophthalate and terephthalate degradation by Comamonas testosteroni YZW-D. Environ Health Perspect. 1995, 103 Suppl 5: 9-12.

    CAS  Article  PubMed  Google Scholar 

  11. 11.

    Takahashi E, Furui M, Seko H, Shibatani T: D-lysine production from L-lysine by successive chemical racemization and microbial asymmetric degradation. Appl Microbiol Biotechnol. 1997, 47 (4): 347-351. 10.1007/s002530050938.

    CAS  Article  PubMed  Google Scholar 

  12. 12.

    Pepper IL, Gentry TJ, Newby DT, Roane TM, Josephson KL: The role of cell bioaugmentation and gene bioaugmentation in the remediation of co-contaminated soils. Environ Health Perspect. 2002, 110 Suppl 6: 943-946.

    Article  PubMed  Google Scholar 

  13. 13.

    Vervaeren H, De Wilde K, Matthys J, Boon N, Raskin L, Verstraete W: Quantification of an Eikelboom type 021N bulking event with fluorescence in situ hybridization and real-time PCR. Appl Microbiol Biotechnol. 2005, Epub ahead of print:

    Google Scholar 

  14. 14.

    Smits TH, Devenoges C, Szynalski K, Maillard J, Holliger C: Development of a real-time PCR method for quantification of the three genera Dehalobacter, Dehalococcoides, and Desulfitobacterium in microbial communities. J Microbiol Methods. 2004, 57 (3): 369-378. 10.1016/j.mimet.2004.02.003.

    CAS  Article  PubMed  Google Scholar 

  15. 15.

    Matsuki T, Watanabe K, Fujimoto J, Takada T, Tanaka R: Use of 16S rRNA gene-targeted group-specific primers for real-time PCR analysis of predominant bacteria in human feces. Appl Environ Microbiol. 2004, 70 (12): 7220-7228. 10.1128/AEM.70.12.7220-7228.2004.

    PubMed Central  CAS  Article  PubMed  Google Scholar 

  16. 16.

    Stubner S: Enumeration of 16S rDNA of Desulfotomaculum lineage 1 in rice field soil by real-time PCR with SybrGreen detection. J Microbiol Methods. 2002, 50 (2): 155-164. 10.1016/S0167-7012(02)00024-6.

    CAS  Article  PubMed  Google Scholar 

  17. 17.

    Amann RI, Ludwig W, Schulze R, Spring S, Moore E, Schleifer KH: rRNA-targeted oligonucleotide probes for the identification of genuine and former pseudomonads. Syst Appl Microbiol. 1996, 19: 501-509.

    CAS  Article  Google Scholar 

  18. 18.

    Braun-Howland EB, Vescio PA, Nierzwicki-Bauer SA: Use of a simplified cell blot technique and 16S rRNA-directed probes for identification of common environmental isolates. Appl Environ Microbiol. 1993, 59 (10): 3219-3224.

    PubMed Central  CAS  PubMed  Google Scholar 

  19. 19.

    Schleifer KH, Amann RI, Ludwig W, Rothemund C, Springer N, Dorn S: Nucleic acid probes for the identification and in situ detection of pseudomonads. Pseudomonas: Molecular Biology and Biotechnology. Edited by: Galli E, Silver S, Withold B. 1992, Washington , American Society for Microbiology, 127-134.

    Google Scholar 

  20. 20.

    Fuchslin HP, Ruegg I, Van Der Meer JR, Egli T: Effect of integration of a GFP reporter gene on fitness of Ralstonia eutropha during growth with 2,4-dichlorophenoxyacetic acid. Environ Microbiol. 2003, 5 (10): 878-887. 10.1046/j.1462-2920.2003.00479.x.

    Article  PubMed  Google Scholar 

  21. 21.

    Bouchez T, Patureau D, Dabert P, Juretschko S, Dore J, Delgenes P, Moletta R, Wagner M: Ecological study of a bioaugmentation failure. Environ Microbiol. 2000, 2 (2): 179-190. 10.1046/j.1462-2920.2000.00091.x.

    CAS  Article  PubMed  Google Scholar 

  22. 22.

    Kuehn M, Hausner M, Bungartz HJ, Wagner M, Wilderer PA, Wuertz S: Automated confocal laser scanning microscopy and semiautomated image processing for analysis of biofilms. Appl Environ Microbiol. 1998, 64 (11): 4115-4127.

    PubMed Central  CAS  PubMed  Google Scholar 

  23. 23.

    Bathe S, Schwarzenbeck N, Hausner M: Plasmid-mediated bioaugmentation of activated sludge bacteria in a sequencing batch moving bed reactor using pNB2. Lett Appl Microbiol. 2005, 41: 242-247. 10.1111/j.1472-765X.2005.01754.x.

    CAS  Article  PubMed  Google Scholar 

  24. 24.

    ProbeBase - an online resource for rRNA-targeted oligonucleotide probes.

  25. 25.

    Bathe S: Conjugal transfer of plasmid pNB2 to activated sludge bacteria leads to 3-chloroaniline degradation in enrichment cultures. Lett Appl Microbiol. 2004, 38 (6): 527-531. 10.1111/j.1472-765X.2004.01532.x.

    CAS  Article  PubMed  Google Scholar 

  26. 26.

    Bathe S, Lebuhn M, Ellwart JW, Wuertz S, Hausner M: High phylogenetic diversity of transconjugants carrying plasmid pJP4 in an activated sludge-derived microbial community. FEMS Microbiol Lett. 2004, 235 (2): 215-219. 10.1111/j.1574-6968.2004.tb09591.x.

    CAS  Article  PubMed  Google Scholar 

  27. 27.

    Klausen M, Heydorn A, Ragas P, Lambertsen L, Aaes-Jorgensen A, Molin S, Tolker-Nielsen T: Biofilm formation by Pseudomonas aeruginosa wild type, flagella and type IV pili mutants. Mol Microbiol. 2003, 48 (6): 1511-1524. 10.1046/j.1365-2958.2003.03525.x.

    CAS  Article  PubMed  Google Scholar 

  28. 28.

    Kaplan N, Zosim Z, Rosenberg E: Reconstitution of emulsifying activity of Acinetobacter calcoaceticus BD4 emulsan by using pure polysaccharide and protein. Appl Environ Microbiol. 1987, 53 (2): 440-446.

    PubMed Central  CAS  PubMed  Google Scholar 

  29. 29.

    Huber B, Riedel K, Kothe M, Givskov M, Molin S, Eberl L: Genetic analysis of functions involved in the late stages of biofilm development in Burkholderia cepacia H111. Mol Microbiol. 2002, 46 (2): 411-426. 10.1046/j.1365-2958.2002.03182.x.

    CAS  Article  PubMed  Google Scholar 

  30. 30.

    Boon N, Goris J, De Vos P, Verstraete W, Top EM: Genetic diversity among 3-chloroaniline- and aniline-degrading strains of the Comamonadaceae. Appl Environ Microbiol. 2001, 67 (3): 1107-1115. 10.1128/AEM.67.3.1107-1115.2001.

    PubMed Central  CAS  Article  PubMed  Google Scholar 

  31. 31.

    Thompson JD, Gibson TJ, Plewniak F, Jeanmougin F, Higgins DG: The CLUSTAL_X windows interface: flexible strategies for multiple sequence alignment aided by quality analysis tools. Nucleic Acids Res. 1997, 25 (24): 4876-4882. 10.1093/nar/25.24.4876.

    PubMed Central  CAS  Article  PubMed  Google Scholar 

  32. 32.

    National Centre for Biotechnology Information.

  33. 33.

    Ribosomal Database Project-II.

  34. 34.

    Ausubel FM, Brent R, Kingson RE, Moore DD, Seidman JG, Smith JA, Struhl K: Short protocols in molecular biology. 1999, New York, USA , Wiley and Sons

    Google Scholar 

  35. 35.

    Devereux R, Willis SG: Amplification of ribosomal RNA sequences. Molecular Microbial Ecology Manual. Edited by: Akkermans ADL, van Elsas JD, De Bruijn FJ. 1995, Dordrecht, The Netherlands , Kluwer, 3.3.1.: 1-11.

    Google Scholar 

  36. 36.

    Amann RI: In situ identification of microorganisms by whole cell hybridization with rRNA-targeted nucleic acid probes. Molecular Microbial Ecology Manual. Edited by: Akkermans ADL, van Elsas JD, de Bruijn FJ. 1995, Dordrecht, The Netherlands , Kluwer, 3.3.6.: 1-15.

    Google Scholar 

  37. 37.

    The EMBL Nucleotide Sequence Database.

  38. 38.

    Amann RI, Binder BJ, Olson RJ, Chisholm SW, Devereux R, Stahl DA: Combination of 16S rRNA-targeted oligonucleotide probes with flow cytometry for analyzing mixed microbial populations. Appl Environ Microbiol. 1990, 56 (6): 1919-1925.

    PubMed Central  CAS  PubMed  Google Scholar 

  39. 39.

    Daims H, Bruhl A, Amann R, Schleifer KH, Wagner M: The domain-specific probe EUB338 is insufficient for the detection of all Bacteria: development and evaluation of a more comprehensive probe set. Syst Appl Microbiol. 1999, 22 (3): 434-444.

    CAS  Article  PubMed  Google Scholar 

Download references


This work was supported by the German Research Foundation (DFG, grant Ha3164/2-2 to MH).

Author information



Corresponding author

Correspondence to Martina Hausner.

Additional information

Authors' contributions

Both authors contributed to experimental design of the project. SB carried out the experimental work and drafted the manuscript. MH revised and finalized the manuscript. All authors read and approved the final manuscript.

Authors’ original submitted files for images

Rights and permissions

This article is published under license to BioMed Central Ltd. This is an Open Access article distributed under the terms of the Creative Commons Attribution License (, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

Reprints and Permissions

About this article

Cite this article

Bathe, S., Hausner, M. Design and evaluation of 16S rRNA sequence based oligonucleotide probes for the detection and quantification of Comamonas testosteroni in mixed microbial communities. BMC Microbiol 6, 54 (2006).

Download citation


  • Testosterone
  • Enrichment Culture
  • Mixed Microbial Community
  • Activate Sludge Bacterium
  • Total Bacterial Cell Number