- Methodology article
- Open Access
Effects of polymerase, template dilution and cycle number on PCR based 16 S rRNA diversity analysis using the deep sequencing method
© Wu et al; licensee BioMed Central Ltd. 2010
- Received: 26 June 2010
- Accepted: 12 October 2010
- Published: 12 October 2010
The primer and amplicon length have been found to affect PCR based estimates of microbial diversity by pyrosequencing, while other PCR conditions have not been addressed using any deep sequencing method. The present study determined the effects of polymerase, template dilution and PCR cycle number using the Solexa platform.
The PfuUltra II Fusion HS DNA Polymerase (Stratagene) with higher fidelity showed lower amount of PCR artifacts and determined lower taxa richness than the Ex Taq (Takara). More importantly, the two polymerases showed different efficiencies for amplifying some of very abundant sequences, and determined significantly different community structures. As expected, the dilution of the DNA template resulted in a reduced estimation of taxa richness, particularly at the 200 fold dilution level, but the community structures were similar for all dilution levels. The 30 cycle group increased the PCR artifacts while comparing to the 25 cycle group, but the determined taxa richness was lower than that of the 25 cycle group. The PCR cycle number did not changed the microbial community structure significantly.
These results highlight the PCR conditions, particularly the polymerase, have significant effect on the analysis of microbial diversity with next generation sequencing methods.
- Operational Taxonomy Unit
- Rarefaction Curve
- Taxon Richness
- Cycle Group
- Template Dilution
Microbial diversity in sediment or soil environments is very high, but the exact number of the taxa richness remains elusive . The estimated bacterial species ranged from nearly 103 to over 106 in a gram of sediment sample. Nevertheless, the figure has never been verified because of the low throughput of the traditional 16 S rRNA clone library method. Determining 16 S rRNA short variable tags using the pyrosequencing provided an unprecedented sequencing depth with tens to hundreds of thousands of tags per sample [4, 5], and the method regenerated people's interest in measuring and comparing the microbial taxa richness in various samples [6–8]. Nevertheless, two major types of problems about the 16 S rRNA pyrosequencing process were shortly revealed.
One was that, in any determined samples, the rarefaction curve, particularly for the unique operational taxonomy units (OTU) (100% similarity), never approached asymptotic. The highest number of sequences for a single sample (442,058) was performed on a deep marine biosphere, but the rarefaction curve of the 0.03 distance OTU (97% similarity) was still increasing steeply . The ever-increasing number of different tags either reflects a real microbial taxa richness being detectable only with a higher sequencing effort, or they are artifacts produced by PCR or sequencing processes. Recently, Quince et al. (2009) found that the base calling error of the pyrosequencing method significantly increased the number of novel unique sequences. Consequently, the escalating number of the unique tag, particularly the singletons (tags occur only once) , might be produced mainly from experimental artifacts of pyrosequencing, rather than from the true diversity; and the pyrosequencing method was suggested to overestimate the taxa richness accordingly [10, 11].
The other type of problems was that the microbial diversity might be skewed by experimental procedures, particularly by PCR. Studies suggested that the PCR primer and amplicon length affected the estimation of species richness and evenness [12, 13], and the primers missed half of rRNA microbial diversity . In addition to primers, the effect of some other PCR conditions, like PCR cycle number, annealing temperature et al., have been evaluated with the traditional 16 S rRNA clone library or fingerprinting methods [9, 14–16], but their effects have never been assessed with any next generation sequencing approach yet.
Very recently, we developed a barcoded Illumina paired end sequencing (BIPES) method to determine the 16 S rRNA V6 tags by pair end sequencing strategy on another next generation sequencing platform, the Illumina systems . In the present study, we report our evaluation of three PCR conditions, namely template dilution, PCR cycle number and polymerase, on the V6 microbial diversity analysis.
Deep sequencing result
Rarefaction curves for PCR replicates showed consistent trajectories for both unique and 0.03 OTUs (Fig. 1), indicating that the PCR and sequencing steps had good reproducibility. The unique curves for A (1 fold diluted template, 30 cycles), B (20 fold diluted template, 30 cycles) and D (20 fold diluted template, 25 cycles) conditions almost overlapped (Fig. 1A), indicating a similar richness of unique V6 tags in above three conditions. The C condition (200 fold diluted template, 30 cycles) showed a lower slope than the above three, indicating that dilution of DNA template from 20 to 200 fold reduced the V6 diversity of the sample. The E condition showed the lowest slop, proving that the polymerase had an obvious effect, as all conditions except polymerase for group E were the same as that for group B.
The 0.03 OTU curves were different with that of the unique OTU (Fig. 1B). The most marked change happened to A, B and D groups, which three showed dissimilar slopes this time. The condition D showed the steepest slope, suggesting that more tags in the group having larger than 3% variance than the other two conditions. The difference between E and B curves for 0.03 OTU was less pronounced than that for the unique OTU, indicating that a proportion of different unique sequences between B and E groups were within 97% similarity, which could possibly be produced by the PCR mutation.
In addition to unique and 0.03 OTUs, we also compared OTUs at 0.05 and 0.10 distances (Additional file 2), and the trends were generally similar to that for 0.03 OTU. Nevertheless, because the larger distance OTUs harbored more varied sequences, the differences between the 5 groups were less obvious.
Abundance of top 300 tags
Microbial community structure
The present study sequenced the 16 S rRNA V6 tags using the Solexa platform, which employed a different base calling procedure with the pyrosequencing . We do not assume that the Solexa platform have a higher sequencing accuracy than the 454. Nevertheless, as the sequencing accuracy of all next generation sequencing methods decreases at the 3' end of the reads , overlapping of the pair end sequencing reads with 5' end sequences obviously increases the accuracy of the final result. Furthermore, we employed a very stringent pipeline to trim the low quality reads, as we removed all tags with mismatches in the overlapped region, mismatches with primers, having any N bases, and very short tags. The large number of tags showing mismatches with primers (52,016) had two resources: (i) the impurity of the primers during primer synthesis; and (ii) sequencing error. We suggest that the first one could be the major reason as the quality checking of the primer using mass spectrum showed that there could be nearly 10% of impure primers in the ultra PAGE purified primers (Additional file 3). We found that removing tags with any N bases was very critical, as the 23,222 tags with N bases formed 16,397 unique sequences. Considering that the final number of unique tags was only 67,826, the tags with N bases could contribute a large number of novel unique sequences, but only as singletons or doubletons, therefore to increase the diversity estimation. Although we may not preclude the sequencing artifacts existing in the final result, we suppose that sequencing error effect has been minimized at the present time and we could explore the PCR effect on the 16 S rRNA deep sequencing methods.
Effect of polymerase
The polymerase showed significant effect on both the taxa richness and community structure analysis in our result. Qiu et al. (2001) compared three enzymes with different processitivity and fidelity. They found that the AmpliTaq showed the lowest number PCR artifacts, but not the enzymes with higher fidelity or processitivity. In our study, the two tested polymerases were high fidelity enzymes. The PfuUltra II Fusion HS DNA Polymerase was suggested to have the highest fidelity (20 fold higher than the conventional Taq) and enhanced processitivity (Stratagene manual). The Ex Taq (Takara) had a 4 fold higher fidelity than the conventional Taq. The rarefaction curves of PfuUltra II at the unique distance showed much lower slopes than that of the Ex Taq, indicating that less PCR artifacts were produced using the PfuUltra II enzymes. In addition, while the determined sequences were grouped into 0.03 OTUs, the slopes of rarefaction curves of the two groups showed less pronounced differences, suggesting that a number of the different tags between the two groups could be PCR artifacts, as PCR mutants were suggested to be within 97% similarity with the original sequence .
A more important finding of the present study was that the two enzymes showed different community structures, besides different rRNA microbial richness. The data showed obviously that the two enzymes had significantly different efficiency for amplifying certain kinds of tags, even for the very abundant sequences. PCR bias was previously attributed to intrinsic differences in the amplification efficiency of templates  or to the primer binding energy and kinetics [9, 20]. Our present study, for the first time, revealed the marked bias induced by different polymerase cocktails. It should be note that there were slight differences of Mg2+ and dNTP concentrations between the two cocktails, but the major factor should be the polymerase. Arezi et al. (2003) found that polymerases showed different efficiencies while amplifying 5 templates varied in length or percentage GC content. The pfu enzyme showed higher efficiency to amplify long templates and high percentage GC content templates. The different efficiently might be related to the processivity, in addition to the proof-reading function of the enzymes . Although both enzymes used in our present study were high-fidelity enzymes, the PfuUltra II Fusion HS DNA Polymerase was suggested to have enhanced processivity; therefore the two enzymes might have different efficiencies for specific sequences. While amplifying the same 16 S rRNA mixture, we can assume that one enzyme might amplify diverse 16 S rRNA tags at similar efficiency, while the other one might be not, and the determined community structures would be different accordingly. We can deduce that the community structure at more specific taxonomic levels, e.g. genus or OTU, will change more obviously than the phylum level, as the abundant tags showed so large variances. Nevertheless, we cannot determine which one of the enzymes reflected the real microbial community structure currently, and studies using known 16 S rRNA amalgam as template are warranted.
Effect of dilution
The present study for the first time explored the effect of template dilution on the microbial diversity analysis. It is well known that different soil or sediment DNA extraction methods yield different amount and purity of DNAs . The residual humus and other contaminants in DNA may inhibit the PCR reaction and the DNA is usually diluted for PCR amplification by try and error. Nevertheless, if the dilution affects the diversity analysis has never been explored before. We discussed the template dilution fold rather than the absolute concentration, because 1 gram of different sediment samples might have very different amount of DNA, which should also be considered while analyzing the microbial diversity.
Dilution of the template obviously reduced the determined taxa richness, particularly from the 20 fold to 200 fold. The effect of dilution from 1 to 20 fold was less obvious than the above situation, indicating that the 1 fold DNA sample might be saturated and could endure a small fold of dilution. On the other hand, template dilution had few impacts on the microbial community structure determination, as the relative abundance of each unique OTU and the phylum structure showed good similarity among A, B and C groups. Therefore, previous studies using fingerprinting methods focusing on the structure of major OTUs should be consistent no matter how the template was diluted.
Effect of cycle number
The effect of PCR cycle number has been determined before. More cycle numbers leads to accumulation of more point mutation artifacts  and people suggested to perform PCR at as few cycle numbers as possible [9, 14]. In the present study, the 30 cycle and 25 cycle conditions showed similar rarefaction curves for the unique OTU, but the curves of the 0.03 OTU were different (Fig. 1). The data indicated that more unique OTUs in the 30 cycle group showed higher than 97% similarity, which might come from the PCR mutation, proving that more cycle numbers caused more point mutations. In addition, we found that less cycle number lead to a higher estimation of taxa richness even with fewer sequences (Table 1).
The cycle number did not show any significant effect on the community structure as some reports [9, 14], which was different with the report that less cycle numbers increased the proportion of predominant groups . It should be noted that the variation of replicate samples was slightly higher in the 25 cycle group, indicating that replicates or combining of different tubes should be performed.
The present study adds to the growing body of evidence that interpreting the results of next generation sequencing, particularly for 16 S rRNA diversity is not as straightforward as previously believed, and is riddled with potential biases. In general, polymerase affected both the diversity richness and community structure analysis; while template dilution and increasing the PCR cycle number reduced the richness, but did not affect community structure. Considering that the sequencing data from different environmental or human microbiome studies may be pooled together for comparing microbial diversity [24, 25], these data should be interpreted carefully. We reiterate that samples should be performed on consistent PCR conditions for comparing microbial diversity, particularly for diversity richness.
The sediment sample was taken from the Mai Po Ramsar wetland in Hong Kong, China. We collected a total of 250 g of four subsamples within 1 m diameter at the edge of the mangrove wetland, pooled them together, mixed them well, and then used 1 g for DNA extraction. The mangrove was vegetated with Kadelia candel and Acanthus ilicifolius. The sediment was collected in Aug 2009, and the DNA was extracted from the fresh sediment using the Ultraclean Soil DNA kit (MoBio, USA). The DNA was quantified using the NanoDrop and the concentration was 34 ng μl-1.
We used the 967F (CNACGCGAAGAACCTTANC) and 1046R (CGACAGCCATGCANCACCT) primers to amplify bacterial 16 S V6 fragments. An 8-digit error-correcting barcode sequence (Table 1) as described by Hamady et al.  was added before the 5' end of the 967F primer. A 2 bp 'GT' linker was added between the barcode and the 5' end of the 967f primer to avoid the potential match of barcode sequence with target 16 S sequences. The ultra PAGE purified primers were ordered from Sangon, China.
For each sample, one tube of PCR was performed. The PCR cycle condition was an initial denaturation at 94°C for 2 min; 25 or 30 cycles of 94°C 30 s, 57°C 30 S and 72°C 30S; and a final extention at 72°C for 5 min. The template dilution fold, the cycle number and the polymerase used were as listed in the table 1. For A, B, C, and D groups, each 20 μl reaction consisted of 2 μl Takara 10× Ex Taq Buffer (Mg2+ plus), 2 μl dNTP Mix (2.5 mM each), 0.5 μl Takara Ex Taq DNA polymerase (2.5 units), 1 μl template DNA, 1 μl 10 μM barcoded primer 967F, 1 μl 10 μM primer 1406R, and 12.5 μl ddH2O. For condition E, each 20 μl reaction consisted of 10 μl PfuUltra II Hotstart 2× Master Mix, 1 μl template DNA, 1 μl 10 μM barcoded primer 967F, 1 μl 10 μM primer 1406R, and 7 μl ddH2O.
Deep sequencing using Solexa GAII
Barcode tagged 16 S V6 PCR products were pooled, purified (QIAquick PCR purification Kit, Qiagen), end repaired, A-tailed and pair-end adaptor ligated (Pair-end library preparation kit, Illumina). After the ligation of the adaptors, the sample was purified and dissolved in 30 μl of elution buffer, and 1 μl was then used as template for 12 cycles of PCR amplification. The PCR product was gel purified (QIAquick gel extraction kit, Qiagen) and directly sequenced using the 75 bp pair-end strategy on the Solexa GA II following the manufacturer's instructions. The base-calling pipeline (version SolexaPipeline-0.3) was used to process the raw fluorescent images and the call sequences.
The paired-end reads were overlapped to assemble the final sequence of V6 tags. The sequencing quality of the Solexa platform decreases near the 3' end. We used the first 60 bp from the 5' end of each read for overlapping assembly. A pair was connected with a minimum overlap length of 5 bp and 0 mismatches in the overlapped region. We further trimmed all tags with any mismatches within primers, with any N bases or less than 35 bp for the V6 regions. The final high quality tags were allocated to each sample according to the barcode sequence.
We performed taxonomic classification by assigning the reads of each sample to the 16 S V6 region database refhvr_V6 and then calculated the Global Alignment for Sequence Taxonomy (GAST) distance  (blastn release:2.2.18, e-value <1e-5, -b 50, http://vamps.mbl.edu/resources/databases.php). The OTU, rarefaction, Chao1 and ACE estimation were analyzed using the mothur (v.1.6.0, http://www.mothur.org/wiki/Main_Page) . We wrote a Perl script to calculate the unique sequences (tags) and their abundance information for analyzing the rank-abundance curve of top abundant tags. The principal component analysis (PCA) was performed using Canoco (Version 4.51). The clustering analysis was performed using Primer 6.0. The sequences were deposited in NCBI Short Read Archive: SRA001401.
The present study was partly supported by the Ph.D. Programs Foundation of the Education Ministry of China (No. 20094433120017), the Natural Science Foundation of China (No. 31040013 and No. 30971193), and the Key Discipline Construction Project under the 3rd stage of "211 Project" Guangdong province (GW201019).
- Hong S, Bunge J, Leslin C, Jeon S, Epstein SS: Polymerase chain reaction primers miss half of rRNA microbial diversity. Isme J. 2009, 3 (12): 1365-1373. 10.1038/ismej.2009.89.View ArticlePubMedGoogle Scholar
- Hong SH, Bunge J, Jeon SO, Epstein SS: Predicting microbial species richness. Proc Natl Acad Sci USA. 2006, 103 (1): 117-122. 10.1073/pnas.0507245102.PubMed CentralView ArticlePubMedGoogle Scholar
- Gans J, Wolinsky M, Dunbar J: Computational improvements reveal great bacterial diversity and high metal toxicity in soil. Science. 2005, 309: 1387-1390. 10.1126/science.1112665.View ArticlePubMedGoogle Scholar
- Huber JA, Mark Welch DB, Morrison HG, Huse SM, Neal PR, Butterfield DA, Sogin ML: Microbial Population Structures in the Deep Marine Biosphere. Science. 2007, 318: 97-100. 10.1126/science.1146689.View ArticlePubMedGoogle Scholar
- Sogin ML, Morrison HG, Huber JA, Welch DM, Huse SM, Neal PR, Arrieta JM, Herndl GJ: Microbial diversity in the deep sea and the underexplored "rare biosphere". Proc Natl Acad Sci USA. 2006, 103: 12115-12120. 10.1073/pnas.0605127103.PubMed CentralView ArticlePubMedGoogle Scholar
- Roesch LFW, Fulthorpe RR, Riva A, Casella G, Hadwin AKM, Kent AD, Daroub SH, Camargo FAO, Farmerie WG, Triplett EW: Pyrosequencing enumerates and contrasts soil microbial diversity. ISME J. 2007, 1: 283-290.PubMed CentralPubMedGoogle Scholar
- Galand PE, Casamayor EO, Kirchman DL, Potvin M, Lovejoy C: Unique archaeal assemblages in the Arctic Ocean unveiled by massively parallel tag sequencing. ISME J. 2009, 3 (7): 860-869. 10.1038/ismej.2009.23.View ArticlePubMedGoogle Scholar
- Tringe SG, Hugenholtz P: A renaissance for the pioneering 16 S rRNA gene. Curr Opin Microbiol. 2008, 11: 442-446. 10.1016/j.mib.2008.09.011.View ArticlePubMedGoogle Scholar
- Acinas SG, Sarma-Rupavtarm R, Klepac-Ceraj V, Polz MF: PCR-induced sequence artifacts and bias: insights from comparison of two 16 S rRNA clone libraries constructed from the same sample. Appl Environ Microbiol. 2005, 71 (12): 8966-8969. 10.1128/AEM.71.12.8966-8969.2005.PubMed CentralView ArticlePubMedGoogle Scholar
- Quince C, Lanzen A, Curtis TP, Davenport RJ, Hall N, Head IM, Read LF, Sloan WT: Accurate determination of microbial diversity from 454 pyrosequencing data. Nat Meth. 2009, 6 (9): 639-641. 10.1038/nmeth.1361.View ArticleGoogle Scholar
- Reeder J, Knight R: The 'rare biosphere': a reality check. Nat Meth. 2009, 6 (9): 636-637. 10.1038/nmeth0909-636.View ArticleGoogle Scholar
- Huber JA, Morrison HG, Huse SM, Neal PR, Sogin ML, Mark Welch DB: Effect of PCR amplicon size on assessments of clone library microbial diversity and community structure. Environ Microbiol. 2009, 11 (5): 1292-1302. 10.1111/j.1462-2920.2008.01857.x.PubMed CentralView ArticlePubMedGoogle Scholar
- Engelbrektson A, Kunin V, Wrighton KC, Zvenigorodsky N, Chen F, Ochman H, Hugenholtz P: Experimental factors affecting PCR-based estimates of microbial species richness and evenness. Isme J. 2010, 4 (5): 642-647. 10.1038/ismej.2009.153.View ArticlePubMedGoogle Scholar
- Sipos R, Szekely AJ, Palatinszky M, Revesz S, Marialigeti K, Nikolausz M: Effect of primer mismatch, annealing temperature and PCR cycle number on 16 S rRNA gene-targetting bacterial community analysis. FEMS Microbiol Ecol. 2007, 60 (2): 341-350. 10.1111/j.1574-6941.2007.00283.x.View ArticlePubMedGoogle Scholar
- Hongoh Y, Yuzawa H, Ohkuma M, Kudo T: Evaluation of primers and PCR conditions for the analysis of 16 S rRNA genes from a natural environment. FEMS Microbiol Lett. 2003, 221 (2): 299-304. 10.1016/S0378-1097(03)00218-0.View ArticlePubMedGoogle Scholar
- Qiu X, Wu L, Huang H, McDonel PE, Palumbo AV, Tiedje JM, Zhou J: Evaluation of PCR-generated chimeras, mutations, and heteroduplexes with 16 S rRNA gene-based cloning. Appl Environ Microbiol. 2001, 67 (2): 880-887. 10.1128/AEM.67.2.880-887.2001.PubMed CentralView ArticlePubMedGoogle Scholar
- Zhou HW, Li DF, Tam NFY, Jiang XT, Zhang H, Sheng HF, Qin J, Liu X, Zou F: BIPES, a cost-effective high-throughput method for assessing microbial diversity. ISME J. 2010, 10.1038/ismej.2010.160.Google Scholar
- Schloss PD, Westcott SL, Ryabin T, Hall JR, Hartmann M, Hollister EB, Lesniewski RA, Oakley BB, Parks DH, Robinson CJ: Introducing mothur: Open Source, Platform-independent, Community-supported Software for Describing and Comparing Microbial Communities. Appl Environ Microbiol. 2009, AEM.01541-01509Google Scholar
- Mardis ER: Next-generation DNA sequencing methods. Annu Rev Genomics Hum Genet. 2008, 9: 387-402. 10.1146/annurev.genom.9.081307.164359.View ArticlePubMedGoogle Scholar
- Suzuki M, Rappe MS, Giovannoni SJ: Kinetic bias in estimates of coastal picoplankton community structure obtained by measurements of small-subunit rRNA gene PCR amplicon length heterogeneity. Appl Environ Microbiol. 1998, 64 (11): 4522-4529.PubMed CentralPubMedGoogle Scholar
- Arezi B, Xing W, Sorge JA, Hogrefe HH: Amplification efficiency of thermostable DNA polymerases. Anal Biochem. 2003, 321 (2): 226-235. 10.1016/S0003-2697(03)00465-2.View ArticlePubMedGoogle Scholar
- Pavlov AR, Pavlova NV, Kozyavkin SA, Slesarev AI: Recent developments in the optimization of thermostable DNA polymerases for efficient applications. Trends Biotechnol. 2004, 22 (5): 253-260. 10.1016/j.tibtech.2004.02.011.View ArticlePubMedGoogle Scholar
- Inceoglu O, Hoogwout EF, Hill P, van Elsas JD: Effect of DNA extraction method on the apparent microbial diversity of soil. Appl Environ Microbiol. 2010Google Scholar
- Auguet JC, Barberan A, Casamayor EO: Global ecological patterns in uncultured Archaea. Isme J. 2010, 4 (2): 182-190. 10.1038/ismej.2009.109.View ArticlePubMedGoogle Scholar
- Santelli CM, Orcutt BN, Banning E, Bach W, Moyer CL, Sogin ML, Staudigel H, Edwards KJ: Abundance and diversity of microbial life in ocean crust. Nature. 2008, 453 (7195): 653-656. 10.1038/nature06899.View ArticlePubMedGoogle Scholar
- Hamady M, Walker JJ, Harris JK, Gold NJ, Knight R: Error-correcting barcoded primers for pyrosequencing hundreds of samples in multiplex. Nat Meth. 2008, 5: 235-237. 10.1038/nmeth.1184.View ArticleGoogle Scholar
- Huse SM, Dethlefsen L, Huber JA, Welch DM, Relman DA, Sogin ML: Exploring microbial diversity and taxonomy using SSU rRNA hypervariable tag sequencing. PLoS Genet. 2008, 4 (11): e1000255-10.1371/journal.pgen.1000255.PubMed CentralView ArticlePubMedGoogle Scholar
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 (http://creativecommons.org/licenses/by/2.0), which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.