PyroTRF-ID: a novel bioinformatics methodology for the affiliation of terminal-restriction fragments using 16S rRNA gene pyrosequencing data
- David G Weissbrodt†1,
- Noam Shani†1,
- Lucas Sinclair2, 3, 5,
- Grégory Lefebvre2, 3, 6,
- Pierre Rossi4,
- Julien Maillard1,
- Jacques Rougemont2, 3 and
- Christof Holliger1Email author
© Weissbrodt et al.; licensee BioMed Central Ltd. 2012
Received: 9 August 2012
Accepted: 18 December 2012
Published: 27 December 2012
In molecular microbial ecology, massive sequencing is gradually replacing classical fingerprinting techniques such as terminal-restriction fragment length polymorphism (T-RFLP) combined with cloning-sequencing for the characterization of microbiomes. Here, a bioinformatics methodology for pyrosequencing-based T-RF identification (PyroTRF-ID) was developed to combine pyrosequencing and T-RFLP approaches for the description of microbial communities. The strength of this methodology relies on the identification of T-RFs by comparison of experimental and digital T-RFLP profiles obtained from the same samples. DNA extracts were subjected to amplification of the 16S rRNA gene pool, T-RFLP with the HaeIII restriction enzyme, 454 tag encoded FLX amplicon pyrosequencing, and PyroTRF-ID analysis. Digital T-RFLP profiles were generated from the denoised full pyrosequencing datasets, and the sequences contributing to each digital T-RF were classified to taxonomic bins using the Greengenes reference database. The method was tested both on bacterial communities found in chloroethene-contaminated groundwater samples and in aerobic granular sludge biofilms originating from wastewater treatment systems.
PyroTRF-ID was efficient for high-throughput mapping and digital T-RFLP profiling of pyrosequencing datasets. After denoising, a dataset comprising ca. 10′000 reads of 300 to 500 bp was typically processed within ca. 20 minutes on a high-performance computing cluster, running on a Linux-related CentOS 5.5 operating system, enabling parallel processing of multiple samples. Both digital and experimental T-RFLP profiles were aligned with maximum cross-correlation coefficients of 0.71 and 0.92 for high- and low-complexity environments, respectively. On average, 63±18% of all experimental T-RFs (30 to 93 peaks per sample) were affiliated to phylotypes.
PyroTRF-ID profits from complementary advantages of pyrosequencing and T-RFLP and is particularly adapted for optimizing laboratory and computational efforts to describe microbial communities and their dynamics in any biological system. The high resolution of the microbial community composition is provided by pyrosequencing, which can be performed on a restricted set of selected samples, whereas T-RFLP enables simultaneous fingerprinting of numerous samples at relatively low cost and is especially adapted for routine analysis and follow-up of microbial communities on the long run.
KeywordsMicrobial ecology T-RFLP Pyrosequencing Digital T-RFLP Bioinformatics methodology
Molecular microbial ecology has become an important discipline in natural and medical sciences. Research on the structure, dynamics and evolution of microbial communities in environmental, human, and engineered systems provides substantial scientific knowledge for understanding the underlying microbial processes, for predicting their behavior, and for controlling, favoring, or suppressing target populations [1, 2].
Different analytical methods have been successively developed for the assessment of microbial communities via profiling or metagenomic approaches . Terminal-restriction fragment length polymorphism (T-RFLP) analysis has been widely used over the last decade for culture-independent assessment of complex microbial community structures [4, 5]. Standardized, robust, and highly reproducible T-RFLP has become the method of choice for community fingerprinting since its automation in capillary electrophoresis devices has enabled the simultaneous analysis of numerous samples at relatively low cost [6–8]. Cloning and sequencing methods have been optimized in parallel for taxonomic affiliation of terminal-restriction fragments (T-RF) [9, 10]. This approach however remains time-consuming and often leads to only partial characterization of the apparent microbial diversity . On the other hand, next-generation sequencing (NGS) technologies have recently been applied for comprehensive high-throughput analyses of microbiomes with reduced sequencing costs [12–16] and high reproducibility . Metagenomics projects have however generated novel requirements in resource and expertise for generating, processing, and interpreting large datasets [18–23]. Overall, ′omics′ technologies challenge the field of bioinformatics to design tailored computing solutions for enhanced production of scientific knowledge from massive datasets. While NGS techniques tend to progressively replace the traditional combination of T-RFLP and cloning-sequencing, recent studies have demonstrated the benefits of using both techniques to complement each other [24–28]. The combination of routine T-RFLP and NGS strategies could offer an efficient trade-off between laboratory efforts required for the in-depth analysis of bacterial communities and the financial and infrastructural costs related to datasets processing.
If T-RFLP and NGS are meant to be used concomitantly for the investigation of microbial systems, one key objective is to link T-RFs to phylotypes. In parallel to early developments of T-RFLP methods, several computational procedures have been proposed to predict T-RF sizes and to phylogenetically affiliate T-RFs. For instance, TAP T-RFLP , TRiFLe  and T-RFPred  have been developed to perform in silico digestion of datasets of 16S rRNA gene sequences, originating mostly from clone libraries or reference public databases. REPK  has been designed to screen for single and combinations of restriction enzymes for the optimization of T-RFLP profiles, and to design experimental strategies. All these programs do not involve comparison of in silico profiles with experimental data.
In the current study, we propose a novel bioinformatics methodology, called PyroTRF-ID, to assign phylogenetic affiliations to experimental T-RFs by coupling pyrosequencing and T-RFLP datasets obtained from the same biological samples. A recent study showing that natural bacterial community structures analyzed with both techniques were very similar  strengthened the here adopted conceptual approach. The methodological objectives were to generate digital T-RFLP (dT-RFLP) profiles from full pyrosequencing datasets, to cross-correlate them to the experimental T-RFLP (eT-RFLP) profiles, and to affiliate eT-RFs to closest bacterial relatives, in a fully automated procedure. The effects of different processing algorithms are discussed. An additional functionality was developed to assess the impact of restriction enzymes on resolution and representativeness of T-RFLP profiles. Validation was conducted with high- and low-complexity bacterial communities. This dual methodology was meant to process single DNA extracts in T-RFLP and pyrosequencing with similar PCR conditions, and therefore aimed to preserve the original microbial complexity of the investigated samples.
Two different biological systems were used for analytical procedure validation. The first set comprised ten groundwater (GRW) samples from two different chloroethene-contaminated aquifers that have been previously described by Aeppli et al.  and Shani . The second set consisted of five aerobic granular sludge (AGS) biofilm samples from anaerobic-aerobic sequencing batch reactors operated for full biological nutrient removal from an acetate-based synthetic wastewater. The AGS system has been described previously  and displayed a lower bacterial community complexity (richness of 42±6 eT-RFs, Shannon′s H′ diversity of 2.5±0.2) than the GRW samples (richness of 67±15 eT-RFs, Shannon′s H′ diversity of 3.3±0.5).
GRW samples were filtered through 0.2-μm autoclaved polycarbonate membranes (Isopore™ Membrane Filters, Millipore) with a mobile filtration system (Filter Funnel Manifolds, Pall Corporation). DNA was extracted using the PowerSoil™ DNA Extraction Kit (Mo-Bio Laboratories, Inc.) following the manufacturer instructions, except that the samples were processed in a bead-beater (Fastprep FP120, Bio101) at 4.5 m·s-1 for 30 s after the addition of solution C1.
DNA from AGS samples was extracted with the automated Maxwell 16 Tissue DNA Purification System (Promega, Duebendorf, Switzerland) according to manufacturer′s instructions with following modifications. An aliquot of 100 mg of ground granular sludge was preliminarily digested during 1 h at 37°C in 500 μL of a solution composed of 5 mg·mL-1 lysozyme in TE buffer (10 mM Tris–HCl, 0.1 mM EDTA, pH 7.5). The DNA extracts were resuspended in 300 μL of TE buffer.
All extracted DNA samples were quantified with the ND-1000 Nanodrop® spectrophotometer (Thermo Fisher Scientific, USA) and stored at −20°C until analysis.
The eT-RFLP analysis of the GRW series was done according to Rossi et al.  with following modifications: (i) 30 μL PCR reactions contained 3 μL 10× Y buffer, 2.4 μL 10 mM dNTPs, 1.5 μL of each primer at 10 μM, 6 μL 5× enhancer P solution, 1.5 U PeqGold Taq polymerase (Peqlab), and 0.2 ng·μL-1 template DNA (final concentration), completed with autoclaved and UV-treated Milli-Q water (Millipore, USA); (ii) for each DNA extract, PCR amplification was carried out in triplicate. Samples from the AGS series were analyzed by eT-RFLP according to Ebrahimi et al.  with following modifications: (i) Go Taq polymerase (Promega, Switzerland) was used for PCR amplification; (ii) forward primer was FAM-labeled; (iii) the PCR program was modified to increase the initial denaturation to 10 min, the cycle denaturation step to 1 min, and 30 cycles of amplification. All PCRs were carried out using the labeled forward primer 8f (FAM-5′-AGAGTTTGATCMTGGCTCAG-3′) and the reverse primer 518r (5′-ATTACCGCGGCTGCTGG-3′). For details, refer to Weissbrodt et al. .
The resulting eT-RFLP profiles were generated between 50 and 500 bp as described in . The eT-RFLP profiles were aligned using the Treeflap crosstab macro  and expressed as relative contributions of operational taxonomic units (OTUs). For GRW samples which exhibited numerous low abundant OTUs, the final bacterial community datasets were constructed as follows: multivariate Ruzicka dissimilarities were computed between replicates of eT-RFLP profiles with R  and the additional package Vegan ; the profile at the centroid (i.e. displaying the lowest dissimilarity with its replicates) was selected for each sample to build the final community profiles. For AGS samples which were characterized by less complex communities, triplicates were periodically measured and resulted in a mean relative standard coefficient of 6% over the analytical method.
Cloning and sequencing
Clone libraries were constructed with the 16S rRNA gene pool amplified from DNA samples using the same PCR procedures as described in the eT-RFLP method but with an unlabeled 8f primer. The PCR products were purified with the purification kit Montage® PCR Centrifugal Filter Devices (Millipore, USA), ligated into pGEM®-T Easy vector (Promega, USA) and transformed into E. coli XL1-Blue competent cells (Agilent Technologies, USA). The eT-RFLP procedure was then applied on isolated colonies in order to screen for the dominant eT-RFs obtained previously by eT-RFLP on the entire 16S rRNA gene pool. Then the 16S rRNA gene was amplified from selected colonies using PCR with primers T7 and SP6 (Promega, USA) and purified as described above. A sequencing reaction was carried out on each purified PCR product as described in . Sequences were aligned in BioEdit , and primer sequences were removed. Sequences were analyzed for chimeras using Bellerophon , and dT-RFs of selected clones were produced by in silico digestion using TRiFLe  for comparison with eT-RFs.
A total of 15 biological samples were analyzed using bacterial tag encoded FLX amplicon pyrosequencing analysis. A first set of DNA extracts from GRW and AGS samples were sent for sequencing to Research and Testing Laboratory LLC (Lubbock, TX, USA). The samples underwent partial amplification of the V1-V3 region of the 16S rRNA gene by PCR with unlabeled 8f and 518r primers, secondary PCR with tagged fusion primers for FLX amplicon sequencing, emulsion-based clonal amplification (emPCR), and GS FLX sequencing targeting at least 3′000 reads with the 454 GS-FLX Titanium Genome Sequencing System technology (Roche, Switzerland). The whole sample preparation protocol has been made available by the company in the publication of Sun et al. . This series refers, in the present study, to the low reads amount pyrosequencing procedure (LowRA). The DNA extract of one AGS sample was analyzed in triplicate through the whole analytical method from pyrosequencing (LowRA) to PyroTRF-ID analysis.
A second set of amplicons from different GRW samples was analyzed by GATC Biotech AG (Konstanz, Germany) following an analog procedure but targeting at least 10′000 reads (referred to as the high reads amount method, HighRA, hereafter). The A- and B-adapters for sequencing with the Roche technology were ligated to the ends of the DNA fragments. The samples were run on a 2% agarose gel with TAE buffer and the band in a size range of 700–900 bp, 450–650 bp, or 100–500 bp, respectively, was excised and column purified. After concentration measurement the differently tagged libraries were pooled. The three resulting library pools were immobilized onto DNA capture beads and the amplicon-beads obtained were amplified through emPCR according to the manufacturer′s recommendations. Following amplification, the emulsion was chemically broken and the beads carrying the amplified DNA library were recovered and washed by filtration. Each pool was sequenced on a quarter GS FLX Pico-Titer plate device with GS FLX Titanium XLR70 chemistry on a GS FLX+ Instrument. The GS FLX System Software Version 2.6 was used and the GS FLX produced the sequence data as Standard Flowgram Format (SFF) file containing flowgrams for each read with basecalls and per-base quality scores.
Development of the PyroTRF-ID bioinformatics methodology
Input 454 tag-encoded pyrosequencing datasets were used either in raw standard flowgram (.sff), or as pre-denoised fasta format (.fasta) as presented below. Input eT-RFLP datasets were provided in coma-separated-values format (.csv).
Sequence denoising was integrated in the PyroTRF-ID workflow but this feature can be disabled by the user. It requires the independent installation of the QIIME software  to decompose and denoise the .sff files containing the whole pyrosequencing information into .sff.txt, .fasta and .qual files. Briefly, the script split_libraries.py was used first to remove tags and primers. Sequences were then filtered based on two criteria: (i) a sequence length ranging from the minimum (default value of 300 bp) and maximum 500-bp amplicon length, and (ii) a PHRED sequencing quality score above 20 according to Ewing and Green . Denoising for the removal of classical 454 pyrosequencing flowgram errors such as homopolymers [45, 46] was carried out with the script denoise_wrapper.py. Denoised sequences were processed using the script inflate_denoiser_output.py in order to generate clusters of sequences with at least 97% identity as conventionally used in the microbial ecology community . Based on computation of statistical distance matrices, one representative sequence (centroid) was selected for each cluster. With this procedure, a new file was created containing cluster centroids inflated according to the original cluster sizes as well as non-clustering sequences (singletons). The denoising step on the HPCC typically lasted approximately 13 h and 5 h for HighRA and LowRA datasets, respectively.
Mapping of sequences was performed using the Burrows-Wheeler Aligner′s Smith-Waterman (BWA-SW) alignment algorithm  against the Greengenes database . The SW score was used as mapping quality criterion [50, 51]. It can be set by the user according to research needs. Sequences with SW scores below 150 were removed from the pipeline. SW cutoffs have typically been used in a range between 100 and 250 [52, 53]. This score can be adapted to reduce the probability of mismatches. SW scores normalized by sequence length were computed to allow comparison between sequences of various lengths. Two files were generated consecutive to mapping. The first one provided general mapping statistics for each sample. The second one provided the list of unmapped sequences, which were removed from the PyroTRF-ID pipeline.
Generation of dT-RFLP profiles
Sequences that passed through all previous steps of the procedure were digested in silico using the restriction enzyme HaeIII which was selected from the Bio.Restriction BioPython database. The dT-RFLP profiles were generated for each sample considering both the size of the dT-RFs and their relative abundance in the sample. Sequences containing no restriction site were discarded. A raw dT-RFLP profile plot was generated as output file. Different restriction enzymes can be tested in the PyroTRF-ID workflow for the optimization of dT-RFLP profiles. This is particularly convenient for designing new eT-RFLP approaches. Such screening can be performed on the pyrosequencing datasets without requirements of eT-RFLP data as input file.
Comparison of eT-RFLP and dT-RFLP profiles
In order to allow comparison with eT-RFLP profiles, T-RFs below 50 bp were removed, and a second set of dT-RFLP profiles was generated. To overcome any possible discrepancy between experimental and in silico T-RFLP , PyroTRF-ID evaluated the most probable drift between e- and dT-RFLP profiles by computing the cross-correlation of the two. A plot showing the results of the cross-correlation was generated in order to help the user assessing the optimal shift to apply for aligning both profiles. By default, PyroTRF-ID corrected the dT-RFLP profile based on the drift with the highest cross-correlation. However, the user can optionally define a specific shift to apply. After shifting the dT-RFLP data, a mirror plot was generated allowing visual comparison of the dT-RFLP and eT-RFLP profiles.
Assignment of affiliation to dT-RFs
Peak annotation files were generated in comma-separated-values format (.csv), listing all digitally obtained T-RFs within each dT-RFLP profile, together with their original and shifted lengths. Closest phylogenetic affiliations were provided together with the number of reads and their relative contribution to the T-RF, as well as with the absolute and normalized SW mapping scores, and the Genbank code of each reference sequence. When eT-RFLP data were not provided in the workflow, the peak annotation file was directly obtained after dT-RFLP processing without removing dT-RFs below 50 bp and without indication of T-RF shift.
Optimization and testing of PyroTRF-ID
Combinations of algorithms tested for the processing of pyrosequencing datasets for dT-RFLP profiling in PyroTRF-ID
Pyrosequencing data processing procedure
Sequence length cut-off
Filtering by SW mapping scoreb
Restriction of sequencesc
1) Standard dT-RFLPd
2) Filtered dT-RFLPe
3) Raw dT-RFLPd
The optimal procedure was then applied for the comparison of PyroTRF-ID results obtained from groundwater and wastewater environments. Finally, restriction enzymes commonly used in T-RFLP analyses of bacterial communities (AluI, HhaI, MspI, RsaI, TaqI, and HaeIII) were selected for comparison of profiling resolutions. Visual observation, richness and diversity indices, as well as density plots were used to analyze the distributions of T-RFs along the e- and dT-RFLP profiles.
Pyrosequencing quality control and read length limitation
The principal quality outputs given by PyroTRF-ID are presented in Additional file 1 for the low throughput (LowRA) and high throughput (HighRA) pyrosequencing methods used in this study. On average, 6′380 and 32′480 reads were obtained for each method, respectively.
Filtering based on the PHRED quality criterion allowed discarding low quality sequences. Most of the remaining sequences had a length below 400–450 bp (Additional file 1a). For the LowRA and HighRA methods, the median number of reads (800 and 2′750) was related to a PHRED score of 30 and 35, respectively, and more than 99% of reads were related to a PHRED score above 20 (Additional file 1b). Only reads longer than 300 bp were conserved for subsequent in silico digestion, because including short sequences in the dT-RFLP profiles may have altered the relative proportions of T-RFs to eT-RFLP profiles. Pyrosequencing datasets obtained with the HighRA method were predominantly composed of short reads below 300 bp (69% of a total of 24′810 reads in the example presented, Additional file 1c). However, 7′641 reads (31%) of high quality sequences were still available for PyroTRF-ID analysis, which was even larger than the number of high quality sequences remaining with the LowRA method (2′804 reads, 47%).
Effect of denoising and mapping procedures
Denoising of pyrosequencing datasets was performed in order to correct for classical 454 analytical errors including the above-mentioned cut-off values: a minimum PHRED quality score of 20, as well as minimum and maximum sequence lengths of 300 and 500 bp, respectively. The denoising process generated a subset of representative sequences harboring at least 3% dissimilarity to each other. This amounted to 17±1% and 43±9% of the number of reads present in the raw datasets obtained with the HighRA and LowRA methods, respectively.
After denoising, the mapping process was the time-limiting step in the PyroTRF-ID pipeline. Twenty minutes were required for mapping the largest datasets against the Greengenes database. Discarding sequences shorter than 300 bp did not lead to a reduced number of detected bacterial phylotypes (Additional file 2). Bacterial community compositions obtained both without and with minimum sequence length cut-off exhibited high correspondences with determination coefficients of R2 between 0.80 and 0.99 depending on the sample type and the reference database used for mapping (Greengenes and RDP). Within the sets of identified phlyotypes, sequences affiliated to Geobacter sp. displayed the highest difference in relative abundance (18%), resulting from a high proportion of short reads below 200 bp in the dataset GRW01.
Phylogenetic annotation of identified T-RFs
Relative contribution to T-RFd(%)
Reference GenBank accession numberg
SW mapping scoreh(−)
Normalized SW mapping scorei(−)
Aerobic granular sludge biofilms from wastewater treatment reactors
S: Rhodocyclus tenuis
S: Rhodocyclus tenuis
S: Rhodocyclus tenuis
S: Rhodocyclus tenuis
S: Rhodocyclus tenuis
Groundwater samples from chloroethene-contaminated aquifers
P: candidate phylum OP3
P: candidate phylum TM7
T-RF diversity for single phylogenetic descriptions
Relative contribution to T-RFc(%)
Reference GenBank accession numbere
SW mapping scoref(−)
Normalized SW mapping scoreg(−)
Flocculent and aerobic granular sludge samples from wastewater treatment systems
Groundwater samples from aquifers contaminated with chloroethenes
Generation of digital T-RFLP profiles
The dT-RFLP profiles were successfully generated with the standard PyroTRF-ID procedure (Table 1) from denoised bacterial pyrosequencing datasets of the GRW and the AGS sample series (Additional file 4). With HaeIII, 165±29 and 87±11 T-RFs were present in the dT-RFLP profiles of the GRW and AGS series, respectively. For all samples, only a reduced number of dT-RFs above 400 bp were obtained because of the low pyrosequencing quality at sequence lengths between 400 and 500 bp.
Comparison of digital and experimental T-RFLP profiles
Cross-correlations between experimental and standard digital T-RFLP profiles
Optimal cross-correlation lag between digital and experimental T-RFLP profilesa(bp)
Maximum cross-correlation coefficient at optimal lagb(−)
Total number of experimental T-RFs per profile (−)
Number of experimental T-RFs affiliated with digital T-RFsc(−)
Percentage of experimental T-RFs affiliated with digital T-RFsc(%)
Aerobic granular sludge
Impact of sequence processing steps, pyrosequencing methods and sample types
The DNA extract of one AGS sample was analyzed in triplicate from pyrosequencing to PyroTRF-ID. The resulting standard dT-RFLP profiles contained 94±10 T-RFs, and exhibited very close diversity indices of 1.48±0.03. In comparison, denoised profiles of all AGS samples collected over 50 days contained similar numbers of T-RFs (84±9) but exhibited quite different diversity indices of 2.12±0.48. There was also very little variation in the cross-correlation coefficients (0.90±0.01) between the dT-RFLP profiles and the corresponding eT-RFLP profile. All three denoised T-RFLP profiles exhibited similar structures, and affiliations were the same for T-RFs that could be identified.
Efficiency of phylogenetic affiliation of T-RFs
Some reference sequences were sometimes represented by several T-RFs (Table 3). For instance, in AGS01, six dT-RFs (34, 194, 213, 214, 220, 247 bp) were affiliated to the same reference sequence of Rhodocyclus tenuis (accession number AB200295), with shifted T-RF 214 being predominant (769 of 844 reads). The Dehalococcoides sp. affiliation in sample GRW05 was related to eight T-RFs, with shifted T-RF 163 being predominant (143 of 156 reads). To investigate this phenomenon, reads resulting in different Dehalococcoides-affiliated T-RFs were retrieved from the pyrosequencing dataset and aligned with ClustalX (Additional file 7). This analysis showed that the multiple T-RF sizes observed were due to reads harboring insertions or deletions of nucleotides before the first HaeIII restriction site or to nucleotide modifications within HaeIII sites.
Advantages and novelties of the PyroTRF-ID bioinformatics methodology
This study describes the development of the PyroTRF-ID bioinformatics methodology for the analysis of microbial community structures, and its application on low- and high-complexity environments. PyroTRF-ID can be seen as the core of a high-throughput methodology for assessing microbial community structures and their dynamics combining NGS technologies and more traditional community fingerprinting techniques such as T-RFLP. More than just predicting the most probable T-RF size of target phylotypes, PyroTRF-ID allows the generation of dT-RFLP profiles from 16S rRNA gene pyrosequencing datasets and the identification of experimental T-RFs by comparing dT-RFLP to eT-RFLP profiles constructed from the same DNA samples.
At the initial stage of the assessment of a microbial community, PyroTRF-ID can be used for the design of an eT-RFLP procedure adapted to a given microbial community through digital screening of restriction enzymes. In contrast to previous studies involving in silico restriction of artificial microbial communities compiled from selected reference sequences from public or cloning-sequencing databases [25, 29, 31], PyroTRF-ID works on sample-based pyrosequencing datasets. This requires the pyrosequencing of a limited number of initial samples. The number of T-RFs, the homogeneity in their distribution, and the number of phylotypes contributing to T-RFs should be used as criteria for the choice of the best suited enzyme. Combination of pyrosequencing and eT-RFLP datasets obtained on the same initial set of samples enables the beginning of the study of new microbial systems with knowledge on T-RFs affiliation. The length of T-RFs and their sequences are directly representative of the investigated sample rather than inferred from existing databases. In this sense, the complexity of the original environment is accurately investigated. For all types of low- and high-complexity environments assessed in this study, HaeIII, AluI and MspI were good candidates for the generation of rich and diverse dT-RFLP profiles.
Subsequently, eT-RFLP can be used as a routine method to assess the dynamics of the stuctures of microbial communites, avoiding the need for systematic pyrosequencing analyses. We suggest that pyrosequencing should be applied at selected time intervals or on representative samples to ensure that the T-RFs still display the same phylogenetic composition. Combining T-RFLP and pyrosequencing is particularly adapted for the temporal follow-up of a microbial system, taking advantage of the relative low costs of T-RFLP and its convenience for routine assessment of microbial community structures, and of the power of pyrosequencing for assessing the composition of these communities. PyroTRF-ID has already been used for the study of bacterial communities involved in start-up of aerobic granular sludge systems  and in natural attenuation of chloroethene-contaminated aquifers .
Performance assessment and limitations of PyroTRF-ID
Classical 454 pyrosequencing errors, such as, inaccurate resolving of homopolymers and single base insertions , were expected to impact the quality of dT-RFLP profiles by overestimating the number of dT-RFs present [55, 56]. The use of a denoising procedure based on the analysis of rank-abundance distributions  was a prerequisite to minimize pyrosequencing errors and to generate dT-RFLP profiles approaching the structure of eT-RFLP profiles, as assessed by the improved cross-correlation coefficients. Filtering pyrosequencing reads with the SW mapping score threshold only slightly reduced overestimations. In addition, this filtering approach does not specifically remove reads based on their intrinsic quality but rather on similarities with existing sequences from the database, hence reducing the complexity of the studied bacterial community to what is already known [54, 57]. When denoising was applied, the use of a SW mapping score threshold did not improve the shape of dT-RFLP profiles. Whereas small-size reads were more abundant in the HighRA pyrosequencing datasets. The pyrosequencing method and the initial amount of reads did not impact the final PyroTRF-ID output. Only the level of complexity of the bacterial communities of the ecosystems could have explained the differences in richness among T-RFLP profiles.
Clipping the low-quality end parts of sequences is an option to improve sequence quality but it is quite improbable that it has an impact on the outcome of the taxon assignment and the creation of dT-RFLP profile. When PyroTRF-ID is run with the “--qiime” option, quality trimming is done using the protocol proposed in QIIME  and its online tutorial (http://qiime.org/tutorials/denoising_454_data.html). This includes the amplicon noise procedure that is efficient in correcting for sequencing errors, PCR single base substitutions, and PCR chimeras . Even if some wrong base calls remain in the consensus sequences after this, they should not affect the assignment to taxon as the BWA aligner can account for mismatches. It should not influence the dT-RFLP profile either since a mismatch outside of the enzyme cleavage site does not affect the length of the fragment produced. As the fragment length is determined by counting the number of base pairs before the enzyme cleavage site and that the BWA aligner does not necessarily use the whole sequence when selecting a match, clipping the low-quality ends of sequences would probably have no measurable effect.
Discrepancies of 0–7 bp between the size of in silico predicted T-RFs and eT-RFs have previously been reported [30, 59]. In the present study, an average discrepancy of 4–6 bp was observed between dT-RFLP and eT-RFLP profiles. This drift was confirmed by comparison of in silico and experimental digestion of 150 clones from a clone library. To overcome the bias induced by the experimental drift, we introduced the calculation of a cross-correlation between dT-RFLP and eT-RFLP profiles. The entire dT-RFLP profile was shifted by the number of base pairs enabling better fitting to the corresponding eT-RFLP profile. It is known that the drift is not constant across the T-RFs but rather depends on the true T-RF length, on its purine content, and on its secondary structure [59–61]. Mirror plots sometimes displayed a 1-bp difference between eT-RFs and dT-RFs. It was crucial for the user to visually inspect the mirror plots prior to semi-manually assigning phylotypes to eT-RFs. The approach adopted here consisted of selecting eT-RFs to identify prior to checking their alignment with dT-RFs. In order to overcome manual inspection, a shift could be computed for each single dT-RF in relation with its sequence composition and theoretical secondary structure . However, the standard deviation associated with this method is still higher than 1 bp. Shifting each single dT-RF based on this function was therefore not expected to improve the alignment accuracy. If at a later stage an improved method for calculating drift for single dT-RFs will be available, it could replace our approach combining a shift of the whole profile, cross-correlation calculation between dT-RFLP and eT-RFLP profiles, and manual inspection. Though user interpretation can introduce a subjective step, final manual processing of T-RFLP profiles can remain the only way to resolve T-RF alignment problems . We nevertheless suggest that selected samples of the investigated system should pass through PyroTRF-ID in triplicates in order to validate the optimal drift determined in the cross-correlation analysis.
Following the standard PyroTRF-ID procedure, high level of correspondence was obtained between dT-RFLP and eT-RFLP profiles. Over all samples, 63±18% of all eT-RFs could be affiliated with a corresponding dT-RF. Correspondence between dT-RFs and eT-RFs was relatively obvious for high abundance T-RFs, in contrast to low abundance dT-RFs. Numerous low abundance dT-RFs were present in dT-RFLP profiles but absent in eT-RFLP profiles. Conversely, eT-RFs were sometimes lacking a corresponding dT-RF. This mainly occurred in profiles generated using pyrosequencing datasets with an initially low amount of reads exceeding 400 bp. The lower proportion of long reads was associated with a decreasing probability of finding a restriction site in the final portion of the sequences. For eT-RFs near 500 bp, incomplete enzymatic restriction could explain that undigested amplicons were detected in the electrophoresis runs [62, 63]. These features, however, do not explain missing dT-RFs, which sometimes occurred in the initial portion of the dT-RFLP profile. Egert and Friedrich  have attributed the presence of ′pseudo T-RFs′ to undigested single stranded DNA amplicons, and have cleared them by cleaving amplicons with single-strand-specific mung bean nuclease. An interesting possibility to increase considerably the number of long reads would be to use bidirectional reads as used by Pilloni et al. for the characterization of tar-oil-degrading microbial communities .
The majority of dT-RFs were affiliated to several phylotypes, revealing the underlying phylogenetic complexity, which was in agreement with Kitts . PyroTRF-ID enabled assessing the relative contributions of each phylotype, and determining the most abundant ones. In most cases, one phylotype clearly displayed the highest number of reads for one dT-RF. However, for some dT-RFs several phylotypes contributed almost equally to the total number of reads. Although problematic while aiming at identifying T-RFs, this information is of primary importance if PyroTRF-ID is intended to be used for designing the most adapted T-RFLP procedure for the study of a particular bacterial community. Finally, as exemplified by Additional file 2, the reference mapping database can have an impact on the identification of T-RFs. A fraction of 35 to 45% of the reads was unassigned during mapping in MG-RAST with the Greengenes database, while only 3-5% was unassigned with RDP. This aspect stresses the need of standardized databases and microbiome dataset processing approaches in the microbial ecology field.
This study presented the successful development of the PyroTRF-ID bioinformatics methodology for high-throughput generation of digital T-RFLP profiles from massive sequencing datasets and for assigning phylotypes to eT-RFs based on pyrosequences obtained from the same samples. In addition, this study leads to the following conclusions:
The combination of pyrosequencing and eT-RFLP data directly obtained from the same samples was a powerful characteristic of the PyroTRF-ID methodology, enabling generation of dT-RFLP profiles that integrate the whole complexity of microbiomes of interest.
The LowRA and HighRA 454 pyrosequencing method did not impact on the final results of the PyroTRF-ID procedure.
As in any new generation sequencing analysis, denoising was a crucial step in the 454 pyrosequencing dataset processing pipeline in order to generate representative digital fingerprints.
The PyroTRF-ID workflow could be applied to the screening of restriction enzymes for the optimization of favorably distributed eT-RFLP profiles by considering the entire underlying microbial communities. HaeIII, MspI and AluI were good candidates for T-RFLP profiling with high richness and diversity indices.
The PyroTRF-ID methodology was validated with different samples from low- and high-complexity environments, and could be implemented in a broad spectrum of biological samples in environmental to medical applications with optimized laboratory and computational costs. This methodology is probably not restricted to pyrosequencing datasets, and could be, after some modifications, applied to datasets obtained with any kind of sequencing techniques.
This research was financed by the Swiss National Science Foundation, Grants No. 120536, 138148 and 120627. We recognize the excellent assistance of Yoan Rappaz in molecular biology analyses. We acknowledge Scot E. Dowd, Yan Sun, Lars Koenig and at Research and Testing Laboratory (Lubbock, Texas, USA), Timothy M. Vogel, Sébastien Cecillon and the Environmental Microbial Genomics Group at Ecole Centrale de Lyon (France), and GATC Biotech (Konstanz, Germany) for pyrosequencing analyses and advice. We are grateful to Ioannis Xenarios for support and access to the Vital-IT HPCC of the Swiss Institute of Bioinformatics (Lausanne, Switzerland).
- Mazzola M: Assessment and management of soil microbial community structure for disease suppression. Annu Rev Phytopathol. 2004, 42 (1): 35-59. 10.1146/annurev.phyto.42.040803.140408.PubMedView ArticleGoogle Scholar
- Kent AD, Yannarell AC, Rusak JA, Triplett EW, McMahon KD: Synchrony in aquatic microbial community dynamics. ISME J. 2007, 1 (1): 38-47. 10.1038/ismej.2007.6.PubMedView ArticleGoogle Scholar
- Gu AZ, Nerenberg R, Sturm BM, Chul P, Goel R: Molecular methods in biological systems. Water Environ Res. 2011, 82 (10): 908-930.View ArticleGoogle Scholar
- Schutte UME, Abdo Z, Bent SJ, Shyu C, Williams CJ, Pierson JD, Forney LJ: Advances in the use of terminal restriction fragment length polymorphism (T-RFLP) analysis of 16S rRNA genes to characterize microbial communities. Appl Microbiol Biotechnol. 2008, 80 (3): 365-380. 10.1007/s00253-008-1565-4.PubMedView ArticleGoogle Scholar
- Marsh TL: Terminal restriction fragment length polymorphism (T-RFLP): an emerging method for characterizing diversity among homologous populations of amplification products. Curr Opin Microbiol. 1999, 2 (3): 323-327. 10.1016/S1369-5274(99)80056-3.PubMedView ArticleGoogle Scholar
- Militsopoulou M, Lamari FN, Hjerpe A, Karamanos NK: Adaption of a fragment analysis technique to an automated high-throughput multicapillary electrophoresis device for the precise qualitative and quantitative characterization of microbial communities. Electrophoresis. 2002, 23 (7–8): 1070-1079.Google Scholar
- Thies JE: Soil microbial community analysis using terminal restriction fragment length polymorphisms. Soil Sci Soc Am J. 2007, 71 (2): 579-591. 10.2136/sssaj2006.0318.View ArticleGoogle Scholar
- Rossi P, Gillet F, Rohrbach E, Diaby N, Holliger C: Statistical assessment of variability of terminal restriction fragment length polymorphism analysis applied to complex microbial communities. Appl Environ Microbiol. 2009, 75 (22): 7268-7270. 10.1128/AEM.00135-09.PubMedPubMed CentralView ArticleGoogle Scholar
- Mengoni A, Grassi E, Bazzicalupo M: Cloning method for taxonomic interpretation of T-RFLP patterns. Biotechniques. 2002, 33 (5): 990-992.PubMedGoogle Scholar
- Grant A, Ogilvie LA: Name that microbe: rapid identification of taxa responsible for individual fragments in fingerprints of microbial community structure. Molecular Ecology Notes. 2004, 4 (1): 133-136. 10.1111/j.1471-8286.2004.00590.x.View ArticleGoogle Scholar
- Mao Y, Yannarell AC, Mackie RI: Changes in N-transforming archaea and bacteria in soil during the establishment of bioenergy crops. PLoS One. 2011, 6 (9): e24750-10.1371/journal.pone.0024750.PubMedPubMed CentralView ArticleGoogle Scholar
- Ronaghi M: Pyrosequencing sheds light on DNA sequencing. Genome Res. 2001, 11 (1): 3-11. 10.1101/gr.11.1.3.PubMedView ArticleGoogle Scholar
- Sun Y, Wolcott RD, Dowd SE: Tag-encoded FLX amplicon pyrosequencing for the elucidation of microbial and functional gene diversity in any environment. Methods Mol Biol. 2011, 733: 129-141. 10.1007/978-1-61779-089-8_9.PubMedView ArticleGoogle Scholar
- Petrosino JF, Highlander S, Luna RA, Gibbs RA, Versalovic J: Metagenomic pyrosequencing and microbial identification. Clin Chem. 2009, 55 (5): 856-866. 10.1373/clinchem.2008.107565.PubMedPubMed CentralView ArticleGoogle 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 (4): 283-290.PubMedPubMed CentralGoogle Scholar
- Wommack KE, Bhavsar J, Ravel J: Metagenomics: read length matters. Appl Environ Microbiol. 2008, 74 (5): 1453-1463. 10.1128/AEM.02181-07.PubMedPubMed CentralView ArticleGoogle Scholar
- Pilloni G, Granitsiotis MS, Engel M, Lueders T: Testing the limits of 454 pyrotag sequencing: reproducibility, quantitative assessment and comparison to T-RFLP fingerprinting of aquifer microbes. PLoS One. 2012, 7 (7): e40467-10.1371/journal.pone.0040467.PubMedPubMed CentralView ArticleGoogle Scholar
- Glenn TC: Field guide to next-generation DNA sequencers. Mol Ecol Resour. 2011, 11 (5): 759-769. 10.1111/j.1755-0998.2011.03024.x.PubMedView ArticleGoogle Scholar
- Trombetti GA, Bonnal RJP, Rizzi E, De Bellis G, Milanesi L: Data handling strategies for high throughput pyrosequencers. BMC Bioinforma. 2007, 8 (1): S22-10.1186/1471-2105-8-S1-S22.View ArticleGoogle Scholar
- Kunin V, Copeland A, Lapidus A, Mavromatis K, Hugenholtz P: A Bioinformatician′s guide to metagenomics. Microbiol Mol Biol Rev. 2008, 72 (4): 557-578. 10.1128/MMBR.00009-08.PubMedPubMed CentralView ArticleGoogle Scholar
- Rodriguez-Ezpeleta N, Hackenberg M, Aransay AM: Bioinformatics for High Throughput Sequencing. 2012, Springer, New YorkView ArticleGoogle Scholar
- Edwards RA: The smallest cells pose the biggest problems: high-performance computing and the analysis of metagenome sequence data. JPCS. 2008, 125: 012050-Google Scholar
- Desai N, Antonopoulos D, Gilbert JA, Glass EM, Meyer F: From genomics to metagenomics. Curr Opin Biotechnol. 2012, 23 (1): 72-76. 10.1016/j.copbio.2011.12.017.PubMedView ArticleGoogle Scholar
- Camarinha-Silva A, Wos-Oxley ML, Jauregui R, Becker K, Pieper DH: Validating T-RFLP as a sensitive and high-throughput approach to assess bacterial diversity patterns in human anterior nares. FEMS Microbiol Ecol. 2012, 79 (1): 98-108. 10.1111/j.1574-6941.2011.01197.x.PubMedView ArticleGoogle Scholar
- Collins RE, Rocap G: REPK: an analytical web server to select restriction endonucleases for terminal restriction fragment length polymorphism analysis. Nucleic Acids Res. 2007, 35 (2): W58-W62.PubMedPubMed CentralView ArticleGoogle Scholar
- Hume ME, Barbosa NA, Dowd SE, Sakomura NK, Nalian AG, Martynova-Van Kley A, Oviedo-Rondon EO: Use of pyrosequencing and denaturing gradient gel electrophoresis to examine the effects of probiotics and essential oil blends on digestive microflora in broilers under mixed eimeria infection. Foodborne Pathog Dis. 2011, 8 (11): 1159-1167. 10.1089/fpd.2011.0863.PubMedView ArticleGoogle Scholar
- Jakobsson HE, Jernberg C, Andersson AF, Sjolund-Karlsson M, Jansson JK, Engstrand L: Short-term antibiotic treatment has differing long-term impacts on the human throat and gut microbiome. PLoS One. 2010, 5 (3): e9836-10.1371/journal.pone.0009836.PubMedPubMed CentralView ArticleGoogle Scholar
- Mushegian AA, Peterson CN, Baker CCM, Pringle A: Bacterial diversity across individual lichens. Appl Environ Microbiol. 2011, 77 (12): 4249-4252. 10.1128/AEM.02850-10.PubMedPubMed CentralView ArticleGoogle Scholar
- Marsh TL, Saxman P, Cole J, Tiedje J: Terminal restriction fragment length polymorphism analysis program, a web-based research tool for microbial community analysis. Appl Environ Microbiol. 2000, 66 (8): 3616-3620. 10.1128/AEM.66.8.3616-3620.2000.PubMedPubMed CentralView ArticleGoogle Scholar
- Junier P, Junier T, Witzel KP: TRiFLe, a program for in silico terminal restriction fragment length polymorphism analysis with user-defined sequence sets. Appl Environ Microbiol. 2008, 74 (20): 6452-6456. 10.1128/AEM.01394-08.PubMedPubMed CentralView ArticleGoogle Scholar
- Fernandez-Guerra A, Buchan A, Mou X, Casamayor EO, Gonzalez JM: T-RFPred: a nucleotide sequence size prediction tool for microbial community description based on terminal-restriction fragment length polymorphism chromatograms. BMC Microbiol. 2010, 10: 262-10.1186/1471-2180-10-262.PubMedPubMed CentralView ArticleGoogle Scholar
- Aeppli C, Hofstetter TB, Amaral HIF, Kipfer R, Schwarzenbach RP, Berg M: Quantifying in situ transformation rates of chlorinated ethenes by combining compound-specific stable isotope analysis, groundwater dating, and carbon isotope mass balances. Environ Sci Technol. 2010, 44 (10): 3705-3711. 10.1021/es903895b.PubMedView ArticleGoogle Scholar
- Shani N: PhD thesis #5379. Assessing the Bacterial Ecology of Organohalide Respiration for the Design of Bioremediation Strategies. 2012, Ecole Polytechnique Fédérale de Lausanne, Lausanne, Switzerland, http://biblion.epfl.ch/EPFL/theses/2012/5379/EPFL_TH5379.pdf,Google Scholar
- Weissbrodt DG, Lochmatter S, Ebrahimi S, Rossi P, Maillard J, Holliger C: Bacterial selection during the formation of early-stage aerobic granules in wastewater treatment systems operated under wash-out dynamics. Front Microbiol. 2012, 3: 332-PubMedPubMed CentralView ArticleGoogle Scholar
- Ebrahimi S, Gabus S, Rohrbach-Brandt E, Hosseini M, Rossi P, Maillard J, Holliger C: Performance and microbial community composition dynamics of aerobic granular sludge from sequencing batch bubble column reactors operated at 20°C, 30°C, and 35°C. Appl Microbiol Biotechnol. 2010, 87: 1555-1568. 10.1007/s00253-010-2621-4.PubMedView ArticleGoogle Scholar
- Rees G, Baldwin D, Watson G, Perryman S, Nielsen D: Ordination and significance testing of microbial community composition derived from terminal restriction fragment length polymorphisms: application of multivariate statistics. Antonie Van Leeuwenhoek. 2004, 86 (4): 339-347. 10.1007/s10482-004-0498-x.PubMedView ArticleGoogle Scholar
- R Development Core Team: R: A language and environment for statistical computing. 2008, R Foundation for Statistical Computing, Vienna, Austria, [http://cran.r-project.org/]Google Scholar
- Oksanen J, Kindt R, Legendre P, O′Hara B, Simpson GL, Solymos P, Stevens MHH, Wagner H: vegan: Community Ecology Package. R package version 1.15-4. 2009, R Foundation for Statistical Computing, Vienna, Austria, [http://CRAN.R-project.org/package=vegan]Google Scholar
- Regeard C, Maillard J, Holliger C: Development of degenerate and specific PCR primers for the detection and isolation of known and putative chloroethene reductive dehalogenase genes. J Microbiol Methods. 2004, 56 (1): 107-118. 10.1016/j.mimet.2003.09.019.PubMedView ArticleGoogle Scholar
- Hall TA: BioEdit: a user-friendly biological sequence alignment editor and analysis program for windows 95/98/NT. Nucleic Acids Symp Ser. 1999, 41: 95-98.Google Scholar
- Huber T, Faulkner G, Hugenholtz P: Bellerophon: a program to detect chimeric sequences in multiple sequence alignments. Bioinformatics. 2004, 20 (14): 2317-2319. 10.1093/bioinformatics/bth226.PubMedView ArticleGoogle Scholar
- Field D, Tiwari B, Booth T, Houten S, Swan D, Bertrand N, Thurston M: Open software for biologists: from famine to feast. Nat Biotechnol. 2006, 24 (7): 801-803. 10.1038/nbt0706-801.PubMedView ArticleGoogle Scholar
- Caporaso JG, Kuczynski J, Stombaugh J, Bittinger K, Bushman FD, Costello EK, Fierer N, Pena AG, Goodrich JK, Gordon JI, et al: QIIME allows analysis of high-throughput community sequencing data. Nat Methods. 2010, 7 (5): 335-336. 10.1038/nmeth.f.303.PubMedPubMed CentralView ArticleGoogle Scholar
- Ewing B, Green P: Base-calling of automated sequencer traces using phred. II. Error probabilities. Genome Res. 1998, 8 (3): 186-194.PubMedView ArticleGoogle Scholar
- Balzer S, Malde K, Jonassen I: Systematic exploration of error sources in pyrosequencing flowgram data. Bioinformatics. 2011, 27 (13): i304-i309. 10.1093/bioinformatics/btr251.PubMedPubMed CentralView ArticleGoogle 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 Methods. 2009, 6 (9): 639-641. 10.1038/nmeth.1361.PubMedView ArticleGoogle Scholar
- Reeder J, Knight R: Rapidly denoising pyrosequencing amplicon reads by exploiting rank-abundance distributions. Nat Methods. 2010, 7 (9): 668-669.PubMedPubMed CentralView ArticleGoogle Scholar
- Li H, Durbin R: Fast and accurate long-read alignment with burrows-wheeler transform. Bioinformatics. 2010, 26 (5): 589-595. 10.1093/bioinformatics/btp698.PubMedPubMed CentralView ArticleGoogle Scholar
- McDonald D, Price MN, Goodrich J, Nawrocki EP, Desantis TZ, Probst A, Andersen GL, Knight R, Hugenholtz P: An improved greengenes taxonomy with explicit ranks for ecological and evolutionary analyses of bacteria and archaea. ISME J. 2012, 6: 610-618. 10.1038/ismej.2011.139.PubMedPubMed CentralView ArticleGoogle Scholar
- Smith TF, Waterman MS: Identification of common molecular subsequences. J Mol Biol. 1981, 147 (1): 195-197. 10.1016/0022-2836(81)90087-5.PubMedView ArticleGoogle Scholar
- Wilson CA, Kreychman J, Gerstein M: Assessing annotation transfer for genomics: quantifying the relations between protein sequence, structure and function through traditional and probabilistic scores. J Mol Biol. 2000, 297 (1): 233-249. 10.1006/jmbi.2000.3550.PubMedView ArticleGoogle Scholar
- Smit AFA, Hubley R, Green P: RepeatMasker. 2003, Institute for Systems Biology, Seattle, USA, [http://www.repeatmasker.org]Google Scholar
- House CH, Runnegar B, Fitz-Gibbon ST: Geobiological analysis using whole genome-based tree building applied to the bacteria, archaea, and eukarya. Geobiology. 2003, 1: 15-26. 10.1046/j.1472-4669.2003.00004.x.View ArticleGoogle Scholar
- Huse SM, Huber JA, Morrison HG, Sogin ML, Welch DM: Accuracy and quality of massively parallel DNA pyrosequencing. Genome Biol. 2007, 8 (7): R143-10.1186/gb-2007-8-7-r143.PubMedPubMed CentralView ArticleGoogle Scholar
- Kunin V, Engelbrektson A, Ochman H, Hugenholtz P: Wrinkles in the rare biosphere: pyrosequencing errors can lead to artificial inflation of diversity estimates. Environ Microbiol. 2010, 12 (1): 118-123. 10.1111/j.1462-2920.2009.02051.x.PubMedView ArticleGoogle Scholar
- Niu B, Fu L, Sun S, Li W: Artificial and natural duplicates in pyrosequencing reads of metagenomic data. BMC Bioinforma. 2010, 11 (1): 187-10.1186/1471-2105-11-187.View ArticleGoogle Scholar
- Gilbert MTP, Binladen J, Miller W, Wiuf C, Willerslev E, Poinar H, Carlson JE, Leebens-Mack JH, Schuster SC: Recharacterization of ancient DNA miscoding lesions: insights in the era of sequencing-by-synthesis. Nucleic Acids Res. 2007, 35 (1): 1-10.PubMedPubMed CentralView ArticleGoogle Scholar
- Quince C, Lanzen A, Davenport RJ, Turnbaugh PJ: Removing noise from pyrosequenced amplicons. BMC Bioinforma. 2011, 12: 38-10.1186/1471-2105-12-38.View ArticleGoogle Scholar
- Kitts CL: Terminal restriction fragment patterns: a tool for comparing microbial communities and assessing community dynamics. Curr Issues Intest Microbiol. 2001, 2 (1): 17-25.PubMedGoogle Scholar
- Bukovska P, Jelinkova M, Hrselova H, Sykorova Z, Gryndler M: Terminal restriction fragment length measurement errors are affected mainly by fragment length, G plus C nucleotide content and secondary structure melting point. J Microbiol Methods. 2010, 82 (3): 223-228. 10.1016/j.mimet.2010.06.007.PubMedView ArticleGoogle Scholar
- Kaplan CW, Kitts CL: Variation between observed and true terminal restriction fragment length is dependent on true TRF length and purine content. J Microbiol Methods. 2003, 54 (1): 121-125. 10.1016/S0167-7012(03)00003-4.PubMedView ArticleGoogle Scholar
- Osborn AM, Moore ERB, Timmis KN: An evaluation of terminal-restriction fragment length polymorphism (T-RFLP) analysis for the study of microbial community structure and dynamics. Environ Microbiol. 2000, 2 (1): 39-50. 10.1046/j.1462-2920.2000.00081.x.PubMedView ArticleGoogle Scholar
- Clement BG, Kehl LE, DeBord KL, Kitts CL: Terminal restriction fragment patterns (TRFPs), a rapid, PCR-based method for the comparison of complex bacterial communities. J Microbiol Methods. 1998, 31 (3): 135-142. 10.1016/S0167-7012(97)00105-X.View ArticleGoogle Scholar
- Egert M, Friedrich MW: Formation of pseudo-terminal restriction fragments, a PCR-related bias affecting terminal restriction fragment length polymorphism analysis of microbial community structure. Appl Environ Microbiol. 2003, 69 (5): 2555-2562. 10.1128/AEM.69.5.2555-2562.2003.PubMedPubMed CentralView ArticleGoogle Scholar
- Pilloni G, von Netzer F, Engel M, Lueders T: Electron acceptor-dependent identification of key anaerobic toluene degraders at a tar-oil-contaminated aquifer by pyro-SIP. FEMS Microbiol Ecol. 2011, 78 (1): 165-175. 10.1111/j.1574-6941.2011.01083.x.PubMedView ArticleGoogle Scholar
- Meyer F, Paarmann D, D′Souza M, Olson R, Glass EM, Kubal M, Paczian T, Rodriguez A, Stevens R, Wilke A, et al: The metagenomics RAST server - a public resource for the automatic phylogenetic and functional analysis of metagenomes. BMC Bioinforma. 2008, 9: 386-10.1186/1471-2105-9-386.View ArticleGoogle Scholar
- Cole J, Wang Q, Cardenas E, Fish J, Chai B, Farris R, Kulam-Syed-Mohideen A, McGarrell D, Marsh T, Garrity G: The ribosomal database project: improved alignments and new tools for rRNA analysis. Nucleic Acids Res. 2009, 37 (1): D141-D145. 10.1093/nar/gkp686.PubMedPubMed CentralView ArticleGoogle Scholar
- Parks DH, Beiko RG: Identifying biologically relevant differences between metagenomic communities. Bioinformatics. 2010, 26 (6): 715-721. 10.1093/bioinformatics/btq041.PubMedView ArticleGoogle 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.