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Appl Environ Microbiol. 2009 December; 75(23): 7560–7564.
Published online 2009 October 9. doi:  10.1128/AEM.01938-09
PMCID: PMC2786429

Detection and Quantification of Dehalogenimonas and “Dehalococcoides” Populations via PCR-Based Protocols Targeting 16S rRNA Genes[down-pointing small open triangle]

Abstract

Members of the haloalkane dechlorinating genus Dehalogenimonas are distantly related to “Dehalococcoides” but share high homology in some variable regions of their 16S rRNA gene sequences. In this study, primers and PCR protocols intended to uniquely target Dehalococcoides were reevaluated, and primers and PCR protocols intended to uniquely target Dehalogenimonas were developed and tested. Use of the genus-specific primers revealed the presence of both bacterial groups in groundwater at a Louisiana Superfund site.

Dehalococcoides” strains are the only bacteria presently known to reductively dehalogenate the carcinogen vinyl chloride (10-12, 17, 22), and DNA-based approaches have been widely applied to detect and quantify these bacteria in mixed cultures and environmental samples (1, 3, 4, 6, 7, 13, 15, 16, 20). As recently reported, Dehalococcoides strains are the closest previously cultured phylogenetic relatives of Dehalogenimonas lykanthroporepellens strains BL-DC-8 and BL-DC-9T (18, 23). The newly isolated Dehalogenimonas strains, which can reductively dehalogenate a variety of polychlorinated alkanes (e.g., 1,2,3-trichloropropane and 1,2-dichloroethane) but not chlorinated ethenes (e.g., tetrachloroethene and vinyl chloride), however, are only distantly related to Dehalococcoides, with 90% identity in 16S rRNA gene sequences. Research reported here was aimed at (i) reevaluating PCR primers and protocols previously reported as allowing specific detection of Dehalococcoides 16S rRNA gene sequences in light of the 16S rRNA gene sequences of the recently isolated Dehalogenimonas strains and (ii) designing and testing PCR primers and protocols that allow detection and quantification of Dehalogenimonas strains.

Evaluation of Dehalococcoides 16S rRNA gene primer specificity.

Twelve sets of previously published oligonucleotide primers targeting 16S rRNA gene sequences of Dehalococcoides, comprising 18 unique primer sequences, were evaluated (Table (Table1).1). Manual alignment of the Dehalococcoides primer sequences against the 16S rRNA gene sequences of Dehalogenimonas lykanthroporepellens strains BL-DC-8 and BL-DC-9T (GenBank accession no. EU679418 and EU679419) revealed that primers Fp DHC 1, Fp DHC 774, and Rp DHC 806 (Table (Table1)1) exactly complement the corresponding binding regions in the 16S rRNA sequences of strains BL-DC-8 and BL-DC-9T. Primer Fp DHC 385 contained a single mismatch. Among the 12 Dehalococcoides primer sets, set D (Table (Table1)1) had the lowest total number of mismatches, with only one base noncomplementary to the 16S rRNA gene sequences of Dehalogenimonas strains.

TABLE 1.
Dehalococcoides-specific 16S rRNA gene primer sets evaluated in this study

To experimentally test whether primers intended to target Dehalococcoides strains would amplify DNA from Dehalogenimonas strains, PCR was performed using the primer sets listed in Table Table1,1, with strain BL-DC-9T genomic DNA as a template. Details regarding genomic DNA preparation and construction of clone DNA from Dehalogenimonas and Dehalococcoides strains are presented as supplemental material. PCR was performed using 25-μl reaction volumes with the same concentrations of primers, Mg2+, and deoxynucleoside triphosphates; thermal conditions; and cycle numbers as those specified in the original publications (Table (Table1).1). Hendrickson et al. (13) reported a range of 30 to 40 cycles, and the mid-range of 35 cycles was used in reactions testing primer sets A to G. AmpliTaq Gold DNA polymerase (Applied Biosystems, Foster City, CA) was used with activation at 95°C for 10 min. Following PCR, reaction products were electrophoresed in a 3% low-melting-temperature agarose gel (ISC BioExpress, Kaysville, UT), stained with ethidium bromide, and imaged.

PCR products of the sizes expected on the basis of 16S rRNA gene sequences of Dehalogenimonas and Dehalococcoides strains were observed for reactions employing the reportedly Dehalococcoides-specific A, D, and E primer sets, with Dehalogenimonas strain BL-DC-9T genomic DNA as a template (see Fig. S1A in the supplemental material). Amplicons were also observed in additional PCRs, performed using plasmid DNA containing a partial 16S rRNA gene insert from strain BL-DC-9T as a template, excluding the possibility that contamination of Dehalococcoides in strain BL-DC-9T genomic DNA preparations might have resulted in PCR product formation. This demonstrates that some previously reported Dehalococcoides-specific primer sets in conjunction with their reported PCR thermal programs can amplify Dehalogenimonas sp. DNA and are therefore not specific to Dehalococcoides.

Additional experiments performed using the same primers and reagent concentrations as those mentioned above but at successively higher annealing temperatures revealed that annealing temperatures of 62, 68, and 66°C for Dehalococcoides primer sets A, D, and E, respectively, did not result in detectable PCR amplification of Dehalogenimonas strain BL-DC-9T DNA but did produce amplicons in reactions using plasmid DNA from Dehalococcoides clone DHC-4 as a template (see Fig. S1B in the supplemental material). This demonstrated that the primer sets can allow specific detection of Dehalococcoides 16S rRNA genes if annealing temperatures are sufficiently high.

It appears that the amplification of Dehalogenimonas 16S rRNA genes by use of Dehalococcoides primers was influenced more by the locations of the mismatches than by the total number of mismatches in the primer/DNA sequence. For example, primer sets A and E both have combined totals of five base mismatches relative to the sequence of strain BL-DC-9T. The mismatches, however, are not located at the priming ends. This allowed amplification of Dehalogenimonas 16S rRNA genes when the relatively low annealing temperature of 55°C was employed. In contrast, although primer set I has only two mismatches relative to the sequence of Dehalogenimonas strain BL-DC-9T, no amplification was observed with annealing at 59°C. This likely resulted because the two mismatches are located at the priming ends (Table (Table11).

16S rRNA gene primers targeting Dehalogenimonas sp.

Details of the methodology used to design primers intended to target 16S rRNA gene sequences unique to Dehalogenimonas are given in the supplemental material. Thirteen primer combinations (Table (Table2)2) were experimentally tested. In initial tests for verification of primer function, genomic DNA from strain BL-DC-9T was used as a template in PCR. Each reaction mixture contained 0.5 μM each primer, 2.5 mM MgCl2, 100 μM each deoxynucleoside triphosphate, and 2 U of AmpliTaq Gold in 1× PCR gold buffer (Applied Biosystems). The thermal program included initial denaturation at 95°C for 10 min; followed by 35 cycles of 1.0 min at 94°C, 45 s at 63°C, and 1.0 min at 72°C; and a final extension step of 10 min at 72°C. All 13 primer combinations intended to specifically target 16S rRNA gene sequences of Dehalogenimonas strains (Table (Table2)2) produced bands with the expected sizes in PCRs with strain BL-DC-9T genomic DNA used as the template (see Fig. S2A in the supplemental material). No PCR products were observed for reactions with plasmid DNA from Dehalococcoides clone DHC-4 used as the template under identical PCR conditions (data not shown), indicating that the primer sets intended to target Dehalogenimonas strains did not amplify DNA from Dehalococcoides strains.

TABLE 2.
Sequences of Dehalogenimonas-specific 16S rRNA gene primers employed in this study

Environmental samples.

Groundwater was collected from eight wells (identification no. W-0627-2, W-0721-1, W-0726-4, W-0820-1, W-0822-3, W-0823-2, W-0825-1, and W-0828-1) at the PetroProcessors of Louisiana, Inc. Superfund site, where contaminants remain in the subsurface as dense nonaqueous-phase liquid (DNAPL), and high concentrations of chlorinated solvents, including 1,1,2-trichloroethane, 1,2-dichloroethane, 1,2-dichloropropane, and vinyl chloride, are present in the aqueous phase (1). All eight groundwater samples, collected in sterile 1.0-liter glass bottles, were visually observed to contain DNAPL. After transport to the laboratory on ice (approximately 1 h), a 30-ml volume of groundwater from each well was mixed with 10 ml TE buffer (10 mM Tris, 1 mM EDTA, pH 8.0) and centrifuged for 10 min at 3,200 × g, the supernatant was decanted, and then DNA was extracted and purified as described previously (1).

DNA extracted from one groundwater sample (W-0823-2) served as the template in separate PCRs using all 13 primer combinations listed in Table Table2.2. All 13 primer sets yielded PCR products of the sizes expected on the basis of the 16S rRNA gene sequences of strains BL-DC-8 and BL-DC-9T (see Fig. S2B in the supplemental material). Sequencing determined that all 13 PCR products were identical to the 16S rRNA gene sequences of Dehalogenimonas strains BL-DC-8 and BL-DC-9T, providing an indication of primer specificity.

DNA extracts from all eight groundwater samples were used as a template in separate PCRs with primer set X (Table (Table2),2), targeting Dehalogenimonas spp., and primer set J (Table (Table1),1), targeting Dehalococcoides spp., as described above. The annealing temperatures were 63°C and 56°C for reactions using primer sets X and J, respectively. For cases where no amplification products were detected, nested PCR was employed with initial amplification using universal bacterial primers 530f/900r (14) with the PCR reagent composition and conditions described above but with an annealing temperature of 56°C. PCR products purified using an UltraClean PCR cleanup kit (MoBio) were then used as a template in a second reaction, using primer set X or J.

PCR products corresponding to Dehalogenimonas 16S rRNA gene sequences were detected in seven groundwater samples, and Dehalococcoides 16S rRNA gene sequences were detected in six samples (see Fig. S3 in the supplemental material). Sequencing of PCR products generated using Dehalococcoides primer set J revealed that amplicons shared 100% identity with sequences of Dehalococcoides strains BAV1, FL2, CBDB1, and 195 (GenBank accession no. AY165308, AF357918, AF230641, and AF004928, respectively), which are identical over the region amplified. The amplicons generated using Dehalogenimonas-targeting primer set X with groundwater DNA extracts from six wells were identical to the 16S rRNA gene sequence of strain BL-DC-9T. The PCR products from the other well had three nucleotide mismatches relative to strain BL-DC-9T.

qPCR.

Dehalogenimonas-targeting primer set X (Table (Table2)2) and Dehalococcoides-targeting primer set J (Table (Table1)1) were used in quantitative real-time PCR (qPCR) to evaluate concentrations of putative dehalogenating bacteria in groundwater samples. To allow calculation of abundance relative to total bacterial populations, universal bacterial primers Bac1055YF/Bac1392R (20) were employed to quantify total bacterial 16S rRNA gene copies. Details regarding qPCR experimental methods and data analysis are provided as supplemental material.

In qPCR, amplicons corresponding to 16S rRNA gene sequences of Dehalogenimonas strains were detected in all eight groundwater samples analyzed, with concentrations ranging from (1.33 ± 0.09) × 102 to (1.88 ± 0.07) × 106 copies/ml (Fig. (Fig.1).1). Dehalococcoides 16S rRNA genes were detected in six groundwater samples; however, concentrations were below the linear range of the calibration curve for all but two samples. The concentrations ranged from <2.8 × 103 copies/ml (i.e., below linear range of the calibration curve) to (5.84 ± 0.20) × 105/ml. The highest concentrations of both Dehalogenimonas and Dehalococcoides strains were in the sample from well W-0823-2, with concentrations of (1.88 ± 0.07) × 106 and (5.84 ± 0.20) × 105 16S rRNA gene copies/ml, respectively. PCR amplicons generated using primer sets X and J each produced a single melting curve peak, further indicating primer specificity in analysis of these environmental samples (data not shown). Total bacterial 16S rRNA gene copies in the groundwater samples ranged from (8.40 ± 1.25) × 103 to (2.38 ± 0.86) × 107 copies/ml (Fig. (Fig.1).1). The upper end of this range is consistent with the observation of >3 × 107 cells/ml groundwater in direct microscopic counts in a previous study of the DNAPL source zone at this site (1).

FIG. 1.
qPCR quantification of total bacteria and Dehalogenimonas and Dehalococcoides 16S rRNA gene copies in groundwater samples from the DNAPL source zone at the PetroProcessors of Louisiana, Inc., Superfund site. Asterisks denote the quantification limit for ...

For well W-0828-1, gene copy numbers determined using Dehalogenimonas-targeting primers were equal to 18.6% of total bacterial 16S rRNA gene copies. Such high relative abundance of dehalogenating bacteria has previously been reported only for enrichment cultures provided with a readily available supply of electron donors (e.g., H2) and other favorable growth conditions (1, 6, 9, 19). In other wells, Dehalogenimonas 16S rRNA gene copy numbers represented smaller percentages of the total bacterial 16S rRNA gene copies, 0.0014 to 9.23%. Dehalococcoides 16S rRNA gene copies in the two samples falling within the linear range of the qPCR calibration curve comprised 0.02 and 2.87% of total bacterial 16S rRNA gene copies.

This study demonstrated the presence of Dehalogenimonas strains with Dehalococcoides strains in groundwater from a DNAPL source zone for the first time. Detection of both bacterial groups, neither of which is known to grow in the absence of chlorinated solvents, supports the notions that (i) dechlorinating bacteria may reside in close proximity to DNAPLs (2, 5, 21, 24) and (ii) dechlorination may involve multiple dehalogenating populations (8). It also expands the genera implicated in multispecies dechlorinating populations to include Dehalogenimonas. Primers reported here for Dehalogenimonas and protocols that were found here to allow unique detection of Dehalococcoides will prove useful in future studies for detection and quantification of these taxa.

Supplementary Material

[Supplemental material]

Acknowledgments

This research was funded by the Governor's Biotechnology Initiative of the Louisiana Board of Regents (grant BOR#015) and NPC Services, Inc. The DNA sequences of Dehalogenimonas-specific PCR primers are the subject matter of U.S. patent application USSN 60/884,593 (W. M. Moe, F. A. Rainey, B. A. Rash, and J. Yan, U.S. Patent Office, 2008).

Footnotes

[down-pointing small open triangle]Published ahead of print on 9 October 2009.

Supplemental material for this article may be found at http://aem.asm.org/.

REFERENCES

1. Bowman, K. S., W. M. Moe, B. A. Rash, H. S. Bae, and F. A. Rainey. 2006. Bacterial diversity of an acidic Louisiana groundwater contaminated by dense nonaqueous-phase liquid containing chloroethanes and other solvents. FEMS Microbiol. Ecol. 58:120-133. [PubMed]
2. Cope, N., and J. B. Hughes. 2001. Biologically-enhanced removal of PCE from NAPL source zones. Environ. Sci. Technol. 35:2014-2021. [PubMed]
3. Cupples, A. M., A. M. Spormann, and P. L. McCarty. 2003. Growth of a Dehalococcoides-like microorganism on vinyl chloride and cis-dichloroethene as electron acceptors as determined by competitive PCR. Appl. Environ. Microbiol. 69:953-959. [PMC free article] [PubMed]
4. Cupples, A. M. 2008. Real-time PCR quantification of Dehalococcoides populations: methods and applications. J. Microbiol. Methods 72:1-11. [PubMed]
5. Dennis, P. C., B. E. Sleep, R. R. Fulthorpe, and S. N. Liss. 2003. Phylogenetic analysis of bacterial populations in an anaerobic microbial consortium capable of degrading saturation concentrations of tetrachloroethylene. Can. J. Microbiol. 49:15-27. [PubMed]
6. Duhamel, M., K. Mo, and E. A. Edwards. 2004. Characterization of a highly enriched Dehalococcoides-containing culture that grows on vinyl chloride and trichloroethene. Appl. Environ. Microbiol. 70:5538-5545. [PMC free article] [PubMed]
7. Fennell, D. E., A. B. Carroll, J. M. Gossett, and S. H. Zinder. 2001. Assessment of indigenous reductive dechlorination potential at a TCE-contaminated site using microcosms, polymerase chain reaction analyses and site data. Environ. Sci. Technol. 35:1830-1839. [PubMed]
8. Grostern, A., and E. A. Edwards. 2006. Growth of Dehalobacter and Dehalococcoides spp. during degradation of chlorinated ethanes. Appl. Environ. Microbiol. 72:428-436. [PMC free article] [PubMed]
9. Gu, A. Z., B. P. Hedlund, J. T. Staley, S. E. Strand, and H. D. Stensel. 2004. Analysis and comparison of the microbial community structures of two enrichment cultures capable of reductively dechlorinating TCE and cis-DCE. Environ. Microbiol. 6:45-54. [PubMed]
10. He, J., K. M. Ritalahti, M. R. Aiello, and F. E. Löffler. 2003. Complete detoxification of vinyl chloride by an anaerobic enrichment culture and identification of the reductively dechlorinating population as a Dehalococcoides species. Appl. Environ. Microbiol. 69:996-1003. [PMC free article] [PubMed]
11. He, J., K. M. Ritalahti, K. L. Yang, S. S. Koenigsberg, and F. E. Löffler. 2003. Detoxification of vinyl chloride to ethene coupled to growth of an anaerobic bacterium. Nature 424:62-65. [PubMed]
12. He, J., Y. Sung, R. Krajmalnik-Brown, K. M. Ritalahti, and F. E. Löffler. 2005. Isolation and characterization of Dehalococcoides sp. strain FL2, a trichloroethene (TCE), and 1,2-dichloroethene-respring anaerobe. Environ. Microbiol. 7:1442-1450. [PubMed]
13. Hendrickson, E. R., J. A. Payne, R. M. Young, M. G. Starr, M. P. Perry, S. Fahnestock, D. E. Ellis, and R. C. Ebersole. 2002. Molecular analysis of Dehalococcoides 16S ribosomal DNA from chloroethene-contaminated sites throughout North America and Europe. Appl. Environ. Microbiol. 68:485-495. [PMC free article] [PubMed]
14. Lane, D. J. 1991. 16S/23S rRNA sequencing, p. 115-175. In E. Stackebrandt and M. Goodfellow (ed.), Nucleic acid techniques in bacterial systematics. John Wiley, Chichester, United Kingdom.
15. Löffler, F. E., Q. Sun, J. Li, and J. M. Tiedje. 2000. 16S rRNA gene-based detection of tetrachloroethene-dechlorinating Desulfuromonas and Dehalococcoides species. Appl. Environ. Microbiol. 66:1369-1374. [PMC free article] [PubMed]
16. Major, D. W., M. L. McMaster, E. E. Cox, E. A. Edwards, S. M. Dworatzek, E. R. Hendrickson, M. G. Starr, J. A. Payne, and L. W. Buonamici. 2002. Field demonstration of successful bioaugmentation to achieve dechlorination of tetrachloroethene to ethene. Environ. Sci. Technol. 36:5106-5116. [PubMed]
17. Maymó-Gatell, X., T. Anguish, and S. H. Zinder. 1999. Reductive dechlorination of chlorinated ethenes and 1,2-dichloroethane by “Dehalococcoides ethenogenes” 195. Appl. Environ. Microbiol. 65:3108-3113. [PMC free article] [PubMed]
18. Moe, W. M., J. Yan, M. F. Nobre, M. S. da Costa, and F. A. Rainey. 2009. Dehalogenimonas lykanthroporepellens gen. nov., sp. nov., a reductive dehalogenating bacterium isolated from chlorinated solvent contaminated groundwater. Int. J. Syst. Evol. Microbiol. [Epub ahead of print.] doi:.10.1099/ijs.0.011502-0 [PubMed] [Cross Ref]
19. Richardson, R. E., V. K. Bhupathiraju, D. L. Song, T. A. Goulet, and L. Alvarez-Cohen. 2002. Phylogenetic characterization of microbial communities that reductively dechlorinate TCE based upon a combination of molecular techniques. Environ. Sci. Technol. 36:2652-2662. [PubMed]
20. Ritalahti, K. M., B. K. Amos, Y. Sung, Q. Z. Wu, S. S. Koenigsberg, and F. E. Löffler. 2006. Quantitative PCR targeting 16S rRNA and reductive dehalogenase genes simultaneously monitors multiple Dehalococcoides strains. Appl. Environ. Microbiol. 72:2765-2774. [PMC free article] [PubMed]
21. Sleep, B. E., D. J. Seepersad, K. Mo, C. M. Heidorn, L. Hrapovic, P. L. Morrill, M. L. McMaster, E. D. Hood, C. Lebron, B. S. Lollar, D. W. Major, and E. A. Edwards. 2006. Biological enhancement of tetrachloroethene dissolution and associated microbial community changes. Environ. Sci. Technol. 40:3623-3633. [PubMed]
22. Sung, Y., K. M. Ritalahti, R. P. Apkarian, and F. E. Löffler. 2006. Quantitive PCR confirms purity of strain GT, a novel trichloroethene-to-ethene-respiring Dehalococcoides isolate. Appl. Environ. Microbiol. 72:1980-1987. [PMC free article] [PubMed]
23. Yan, J., B. A. Rash, F. A. Rainey, and W. M. Moe. 2009. Isolation of novel bacteria within the Chloroflexi capable of reductive dechlorination of 1,2,3-trichloropropane. Environ. Microbiol. 11:833-843. [PubMed]
24. Yang, Y., and P. L. McCarty. 2002. Comparison between donor substrates for biologically enhanced tetrachloroethene DNAPL dissolution. Environ. Sci. Technol. 36:3400-3404. [PubMed]

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