Project FOMC13506_Eduardo services include NGS sequencing of the V1V3 region of the 16S rRNA gene amplicons from the samples. First and foremost, please
download this report, as well as the sequence raw data from the download links provided below.
These links will expire after 60 days. We cannot guarantee the availability of your data after 60 days.
Full Bioinformatics analysis service was requested. We provide many analyses, starting from the raw sequence quality and noise filtering, pair reads merging, as well as chimera filtering for the sequences, using the
DADA2 denosing algorithm and pipeline.
We also provide many downstream analyses such as taxonomy assignment, alpha and beta diversity analyses, and differential abundance analysis.
For taxonomy assignment, most informative would be the taxonomy barplots. We provide an interactive barplots to show the relative abundance of microbes at different taxonomy levels (from Phylum to species) that you can choose.
If you specify which groups of samples you want to compare for differential abundance, we provide both ANCOM and LEfSe differential abundance analysis.
The samples were processed and analyzed with the ZymoBIOMICS® Service: Targeted
Metagenomic Sequencing (Zymo Research, Irvine, CA).
DNA Extraction: If DNA extraction was performed, one of three different DNA
extraction kits was used depending on the sample type and sample volume and were
used according to the manufacturer’s instructions, unless otherwise stated. The kit used
in this project is marked below:
☐
ZymoBIOMICS® DNA Miniprep Kit (Zymo Research, Irvine, CA)
☐
ZymoBIOMICS® DNA Microprep Kit (Zymo Research, Irvine, CA)
☐
ZymoBIOMICS®-96 MagBead DNA Kit (Zymo Research, Irvine, CA)
☑
N/A (DNA Extraction Not Performed)
Elution Volume: 50µL
Additional Notes: NA
Targeted Library Preparation: The DNA samples were prepared for targeted
sequencing with the Quick-16S™ NGS Library Prep Kit (Zymo Research, Irvine, CA).
These primers were custom designed by Zymo Research to provide the best coverage
of the 16S gene while maintaining high sensitivity. The primer sets used in this project
are marked below:
☐
Quick-16S™ Primer Set V1-V2 (Zymo Research, Irvine, CA)
☑
Quick-16S™ Primer Set V1-V3 (Zymo Research, Irvine, CA)
☐
Quick-16S™ Primer Set V3-V4 (Zymo Research, Irvine, CA)
☐
Quick-16S™ Primer Set V4 (Zymo Research, Irvine, CA)
☐
Quick-16S™ Primer Set V6-V8 (Zymo Research, Irvine, CA)
☐
Other: NA
Additional Notes: NA
The sequencing library was prepared using an innovative library preparation process in
which PCR reactions were performed in real-time PCR machines to control cycles and
therefore limit PCR chimera formation. The final PCR products were quantified with
qPCR fluorescence readings and pooled together based on equal molarity. The final
pooled library was cleaned up with the Select-a-Size DNA Clean & Concentrator™
(Zymo Research, Irvine, CA), then quantified with TapeStation® (Agilent Technologies,
Santa Clara, CA) and Qubit® (Thermo Fisher Scientific, Waltham, WA).
Control Samples: The ZymoBIOMICS® Microbial Community Standard (Zymo
Research, Irvine, CA) was used as a positive control for each DNA extraction, if
performed. The ZymoBIOMICS® Microbial Community DNA Standard (Zymo Research,
Irvine, CA) was used as a positive control for each targeted library preparation.
Negative controls (i.e. blank extraction control, blank library preparation control) were
included to assess the level of bioburden carried by the wet-lab process.
Sequencing: The final library was sequenced on Illumina® MiSeq™ with a V3 reagent kit
(600 cycles). The sequencing was performed with 10% PhiX spike-in.
Absolute Abundance Quantification*: A quantitative real-time PCR was set up with a
standard curve. The standard curve was made with plasmid DNA containing one copy
of the 16S gene and one copy of the fungal ITS2 region prepared in 10-fold serial
dilutions. The primers used were the same as those used in Targeted Library
Preparation. The equation generated by the plasmid DNA standard curve was used to
calculate the number of gene copies in the reaction for each sample. The PCR input
volume (2 µl) was used to calculate the number of gene copies per microliter in each
DNA sample.
The number of genome copies per microliter DNA sample was calculated by dividing
the gene copy number by an assumed number of gene copies per genome. The value
used for 16S copies per genome is 4. The value used for ITS copies per genome is 200.
The amount of DNA per microliter DNA sample was calculated using an assumed
genome size of 4.64 x 106 bp, the genome size of Escherichia coli, for 16S samples, or
an assumed genome size of 1.20 x 107 bp, the genome size of Saccharomyces
cerevisiae, for ITS samples. This calculation is shown below:
Calculated Total DNA = Calculated Total Genome Copies × Assumed Genome Size (4.64 × 106 bp) ×
Average Molecular Weight of a DNA bp (660 g/mole/bp) ÷ Avogadro’s Number (6.022 x 1023/mole)
* Absolute Abundance Quantification is only available for 16S and ITS analyses.
The absolute abundance standard curve data can be viewed in Excel here:
The absolute abundance standard curve is shown below:
The complete report of your project, including all links in this report, can be downloaded by clicking the link provided below. The downloaded file is a compressed ZIP file and once unzipped, open the file “REPORT.html” (may only shown as "REPORT" in your computer) by double clicking it. Your default web browser will open it and you will see the exact content of this report.
Please download and save the file to your computer storage device. The download link will expire after 60 days upon your receiving of this report.
Complete report download link:
To view the report, please follow the following steps:
1.
Download the .zip file from the report link above.
2.
Extract all the contents of the downloaded .zip file to your desktop.
3.
Open the extracted folder and find the "REPORT.html" (may shown as only "REPORT").
4.
Open (double-clicking) the REPORT.html file. Your default browser will open the top age of the complete report. Within the
report, there are links to view all the analyses performed for the project.
The raw NGS sequence data is available for download with the link provided below. The data is a compressed ZIP file and can be unzipped to individual sequence files.
Since this is a pair-end sequencing, each of your samples is represented by two sequence files, one for READ 1,
with the file extension “*_R1.fastq.gz”, another READ 2, with the file extension “*_R1.fastq.gz”.
The files are in FASTQ format and are compressed. FASTQ format is a text-based data format for storing both a biological sequence
and its corresponding quality scores. Most sequence analysis software will be able to open them.
The Sample IDs associated with the R1 and R2 fastq files are listed in the table below:
Sample ID
Original Sample ID
Read 1 File Name
Read 2 File Name
F13506.S10
original sample ID here
zr13506_10V1V3_R1.fastq.gz
zr13506_10V1V3_R2.fastq.gz
F13506.S11
original sample ID here
zr13506_11V1V3_R1.fastq.gz
zr13506_11V1V3_R2.fastq.gz
F13506.S12
original sample ID here
zr13506_12V1V3_R1.fastq.gz
zr13506_12V1V3_R2.fastq.gz
F13506.S13
original sample ID here
zr13506_13V1V3_R1.fastq.gz
zr13506_13V1V3_R2.fastq.gz
F13506.S14
original sample ID here
zr13506_14V1V3_R1.fastq.gz
zr13506_14V1V3_R2.fastq.gz
F13506.S15
original sample ID here
zr13506_15V1V3_R1.fastq.gz
zr13506_15V1V3_R2.fastq.gz
F13506.S16
original sample ID here
zr13506_16V1V3_R1.fastq.gz
zr13506_16V1V3_R2.fastq.gz
F13506.S17
original sample ID here
zr13506_17V1V3_R1.fastq.gz
zr13506_17V1V3_R2.fastq.gz
F13506.S18
original sample ID here
zr13506_18V1V3_R1.fastq.gz
zr13506_18V1V3_R2.fastq.gz
F13506.S19
original sample ID here
zr13506_19V1V3_R1.fastq.gz
zr13506_19V1V3_R2.fastq.gz
F13506.S01
original sample ID here
zr13506_1V1V3_R1.fastq.gz
zr13506_1V1V3_R2.fastq.gz
F13506.S20
original sample ID here
zr13506_20V1V3_R1.fastq.gz
zr13506_20V1V3_R2.fastq.gz
F13506.S21
original sample ID here
zr13506_21V1V3_R1.fastq.gz
zr13506_21V1V3_R2.fastq.gz
F13506.S22
original sample ID here
zr13506_22V1V3_R1.fastq.gz
zr13506_22V1V3_R2.fastq.gz
F13506.S23
original sample ID here
zr13506_23V1V3_R1.fastq.gz
zr13506_23V1V3_R2.fastq.gz
F13506.S24
original sample ID here
zr13506_24V1V3_R1.fastq.gz
zr13506_24V1V3_R2.fastq.gz
F13506.S25
original sample ID here
zr13506_25V1V3_R1.fastq.gz
zr13506_25V1V3_R2.fastq.gz
F13506.S26
original sample ID here
zr13506_26V1V3_R1.fastq.gz
zr13506_26V1V3_R2.fastq.gz
F13506.S27
original sample ID here
zr13506_27V1V3_R1.fastq.gz
zr13506_27V1V3_R2.fastq.gz
F13506.S28
original sample ID here
zr13506_28V1V3_R1.fastq.gz
zr13506_28V1V3_R2.fastq.gz
F13506.S29
original sample ID here
zr13506_29V1V3_R1.fastq.gz
zr13506_29V1V3_R2.fastq.gz
F13506.S02
original sample ID here
zr13506_2V1V3_R1.fastq.gz
zr13506_2V1V3_R2.fastq.gz
F13506.S30
original sample ID here
zr13506_30V1V3_R1.fastq.gz
zr13506_30V1V3_R2.fastq.gz
F13506.S31
original sample ID here
zr13506_31V1V3_R1.fastq.gz
zr13506_31V1V3_R2.fastq.gz
F13506.S32
original sample ID here
zr13506_32V1V3_R1.fastq.gz
zr13506_32V1V3_R2.fastq.gz
F13506.S33
original sample ID here
zr13506_33V1V3_R1.fastq.gz
zr13506_33V1V3_R2.fastq.gz
F13506.S34
original sample ID here
zr13506_34V1V3_R1.fastq.gz
zr13506_34V1V3_R2.fastq.gz
F13506.S35
original sample ID here
zr13506_35V1V3_R1.fastq.gz
zr13506_35V1V3_R2.fastq.gz
F13506.S36
original sample ID here
zr13506_36V1V3_R1.fastq.gz
zr13506_36V1V3_R2.fastq.gz
F13506.S37
original sample ID here
zr13506_37V1V3_R1.fastq.gz
zr13506_37V1V3_R2.fastq.gz
F13506.S38
original sample ID here
zr13506_38V1V3_R1.fastq.gz
zr13506_38V1V3_R2.fastq.gz
F13506.S39
original sample ID here
zr13506_39V1V3_R1.fastq.gz
zr13506_39V1V3_R2.fastq.gz
F13506.S03
original sample ID here
zr13506_3V1V3_R1.fastq.gz
zr13506_3V1V3_R2.fastq.gz
F13506.S40
original sample ID here
zr13506_40V1V3_R1.fastq.gz
zr13506_40V1V3_R2.fastq.gz
F13506.S41
original sample ID here
zr13506_41V1V3_R1.fastq.gz
zr13506_41V1V3_R2.fastq.gz
F13506.S42
original sample ID here
zr13506_42V1V3_R1.fastq.gz
zr13506_42V1V3_R2.fastq.gz
F13506.S43
original sample ID here
zr13506_43V1V3_R1.fastq.gz
zr13506_43V1V3_R2.fastq.gz
F13506.S44
original sample ID here
zr13506_44V1V3_R1.fastq.gz
zr13506_44V1V3_R2.fastq.gz
F13506.S45
original sample ID here
zr13506_45V1V3_R1.fastq.gz
zr13506_45V1V3_R2.fastq.gz
F13506.S46
original sample ID here
zr13506_46V1V3_R1.fastq.gz
zr13506_46V1V3_R2.fastq.gz
F13506.S47
original sample ID here
zr13506_47V1V3_R1.fastq.gz
zr13506_47V1V3_R2.fastq.gz
F13506.S48
original sample ID here
zr13506_48V1V3_R1.fastq.gz
zr13506_48V1V3_R2.fastq.gz
F13506.S49
original sample ID here
zr13506_49V1V3_R1.fastq.gz
zr13506_49V1V3_R2.fastq.gz
F13506.S04
original sample ID here
zr13506_4V1V3_R1.fastq.gz
zr13506_4V1V3_R2.fastq.gz
F13506.S50
original sample ID here
zr13506_50V1V3_R1.fastq.gz
zr13506_50V1V3_R2.fastq.gz
F13506.S51
original sample ID here
zr13506_51V1V3_R1.fastq.gz
zr13506_51V1V3_R2.fastq.gz
F13506.S52
original sample ID here
zr13506_52V1V3_R1.fastq.gz
zr13506_52V1V3_R2.fastq.gz
F13506.S53
original sample ID here
zr13506_53V1V3_R1.fastq.gz
zr13506_53V1V3_R2.fastq.gz
F13506.S54
original sample ID here
zr13506_54V1V3_R1.fastq.gz
zr13506_54V1V3_R2.fastq.gz
F13506.S55
original sample ID here
zr13506_55V1V3_R1.fastq.gz
zr13506_55V1V3_R2.fastq.gz
F13506.S56
original sample ID here
zr13506_56V1V3_R1.fastq.gz
zr13506_56V1V3_R2.fastq.gz
F13506.S57
original sample ID here
zr13506_57V1V3_R1.fastq.gz
zr13506_57V1V3_R2.fastq.gz
F13506.S58
original sample ID here
zr13506_58V1V3_R1.fastq.gz
zr13506_58V1V3_R2.fastq.gz
F13506.S59
original sample ID here
zr13506_59V1V3_R1.fastq.gz
zr13506_59V1V3_R2.fastq.gz
F13506.S05
original sample ID here
zr13506_5V1V3_R1.fastq.gz
zr13506_5V1V3_R2.fastq.gz
F13506.S60
original sample ID here
zr13506_60V1V3_R1.fastq.gz
zr13506_60V1V3_R2.fastq.gz
F13506.S61
original sample ID here
zr13506_61V1V3_R1.fastq.gz
zr13506_61V1V3_R2.fastq.gz
F13506.S62
original sample ID here
zr13506_62V1V3_R1.fastq.gz
zr13506_62V1V3_R2.fastq.gz
F13506.S63
original sample ID here
zr13506_63V1V3_R1.fastq.gz
zr13506_63V1V3_R2.fastq.gz
F13506.S64
original sample ID here
zr13506_64V1V3_R1.fastq.gz
zr13506_64V1V3_R2.fastq.gz
F13506.S06
original sample ID here
zr13506_6V1V3_R1.fastq.gz
zr13506_6V1V3_R2.fastq.gz
F13506.S07
original sample ID here
zr13506_7V1V3_R1.fastq.gz
zr13506_7V1V3_R2.fastq.gz
F13506.S08
original sample ID here
zr13506_8V1V3_R1.fastq.gz
zr13506_8V1V3_R2.fastq.gz
F13506.S09
original sample ID here
zr13506_9V1V3_R1.fastq.gz
zr13506_9V1V3_R2.fastq.gz
Please download and save the file to your computer storage device. The download link will expire after 60 days upon your receiving of this report.
DADA2 is a software package that models and corrects Illumina-sequenced amplicon errors.
DADA2 infers sample sequences exactly, without coarse-graining into OTUs,
and resolves differences of as little as one nucleotide. DADA2 identified more real variants
and output fewer spurious sequences than other methods.
DADA2’s advantage is that it uses more of the data. The DADA2 error model incorporates quality information,
which is ignored by all other methods after filtering. The DADA2 error model incorporates quantitative abundances,
whereas most other methods use abundance ranks if they use abundance at all.
The DADA2 error model identifies the differences between sequences, eg. A->C,
whereas other methods merely count the mismatches. DADA2 can parameterize its error model from the data itself,
rather than relying on previous datasets that may or may not reflect the PCR and sequencing protocols used in your study.
DADA2 pipeline includes several tools for read quality control, including quality filtering, trimming, denoising, pair merging and chimera filtering. Below are the major processing steps of DADA2:
Step 1. Read trimming based on sequence quality
The quality of NGS Illumina sequences often decreases toward the end of the reads.
DADA2 allows to trim off the poor quality read ends in order to improve the error
model building and pair mergicing performance.
Step 2. Learn the Error Rates
The DADA2 algorithm makes use of a parametric error model (err) and every
amplicon dataset has a different set of error rates. The learnErrors method
learns this error model from the data, by alternating estimation of the error
rates and inference of sample composition until they converge on a jointly
consistent solution. As in many machine-learning problems, the algorithm must
begin with an initial guess, for which the maximum possible error rates in
this data are used (the error rates if only the most abundant sequence is
correct and all the rest are errors).
Step 3. Infer amplicon sequence variants (ASVs) based on the error model built in previous step. This step is also called sequence "denoising".
The outcome of this step is a list of ASVs that are the equivalent of oligonucleotides.
Step 4. Merge paired reads. If the sequencing products are read pairs, DADA2 will merge the R1 and R2 ASVs into single sequences.
Merging is performed by aligning the denoised forward reads with the reverse-complement of the corresponding
denoised reverse reads, and then constructing the merged “contig” sequences.
By default, merged sequences are only output if the forward and reverse reads overlap by
at least 12 bases, and are identical to each other in the overlap region (but these conditions can be changed via function arguments).
Step 5. Remove chimera.
The core dada method corrects substitution and indel errors, but chimeras remain. Fortunately, the accuracy of sequence variants
after denoising makes identifying chimeric ASVs simpler than when dealing with fuzzy OTUs.
Chimeric sequences are identified if they can be exactly reconstructed by
combining a left-segment and a right-segment from two more abundant “parent” sequences. The frequency of chimeric sequences varies substantially
from dataset to dataset, and depends on on factors including experimental procedures and sample complexity.
Results
1. Read Quality Plots NGS sequence analaysis starts with visualizing the quality of the sequencing. Below are the quality plots of the first
sample for the R1 and R2 reads separately. In gray-scale is a heat map of the frequency of each quality score at each base position. The mean
quality score at each position is shown by the green line, and the quartiles of the quality score distribution by the orange lines.
The forward reads are usually of better quality. It is a common practice to trim the last few nucleotides to avoid less well-controlled errors
that can arise there. The trimming affects the downstream steps including error model building, merging and chimera calling. FOMC uses an empirical
approach to test many combinations of different trim length in order to achieve best final amplicon sequence variants (ASVs), see the next
section “Optimal trim length for ASVs”.
2. Optimal trim length for ASVs The final number of merged and chimera-filtered ASVs depends on the quality filtering (hence trimming) in the very beginning of the DADA2 pipeline.
In order to achieve highest number of ASVs, an empirical approach was used -
Create a random subset of each sample consisting of 5,000 R1 and 5,000 R2 (to reduce computation time)
Trim 10 bases at a time from the ends of both R1 and R2 up to 50 bases
For each combination of trimmed length (e.g., 300x300, 300x290, 290x290 etc), the trimmed reads are
subject to the entire DADA2 pipeline for chimera-filtered merged ASVs
The combination with highest percentage of the input reads becoming final ASVs is selected for the complete set of data
Below is the result of such operation, showing ASV percentages of total reads for all trimming combinations (1st Column = R1 lengths in bases; 1st Row = R2 lengths in bases):
R1/R2
281
271
261
251
241
231
321
76.95%
77.01%
77.08%
77.04%
76.96%
64.90%
311
77.18%
77.29%
77.33%
77.38%
65.42%
53.47%
301
77.25%
77.25%
77.33%
65.37%
53.51%
39.50%
291
80.45%
80.57%
68.65%
56.80%
42.82%
41.45%
281
76.61%
64.70%
52.98%
39.07%
37.85%
37.63%
271
64.26%
52.44%
38.72%
37.88%
37.25%
36.95%
Based on the above result, the trim length combination of R1 = 291 bases and R2 = 271 bases (highlighted red above), was chosen for generating final ASVs for all sequences.
This combination generated highest number of merged non-chimeric ASVs and was used for downstream analyses, if requested.
3. Error plots from learning the error rates
After DADA2 building the error model for the set of data, it is always worthwhile, as a sanity check if nothing else, to visualize the estimated error rates.
The error rates for each possible transition (A→C, A→G, …) are shown below. Points are the observed error rates for each consensus quality score.
The black line shows the estimated error rates after convergence of the machine-learning algorithm.
The red line shows the error rates expected under the nominal definition of the Q-score.
The ideal result would be the estimated error rates (black line) are a good fit to the observed rates (points), and the error rates drop
with increased quality as expected.
Forward Read R1 Error Plot
Reverse Read R2 Error Plot
The PDF version of these plots are available here:
4. DADA2 Result Summary The table below shows the summary of the DADA2 analysis,
tracking paired read counts of each samples for all the steps during DADA2 denoising process -
including end-trimming (filtered), denoising (denoisedF, denoisedF), pair merging (merged) and chimera removal (nonchim).
Sample ID
F13506.S01
F13506.S02
F13506.S03
F13506.S04
F13506.S05
F13506.S06
F13506.S07
F13506.S08
F13506.S09
F13506.S10
F13506.S11
F13506.S12
F13506.S13
F13506.S14
F13506.S15
F13506.S16
F13506.S17
F13506.S18
F13506.S19
F13506.S20
F13506.S21
F13506.S22
F13506.S23
F13506.S24
F13506.S25
F13506.S26
F13506.S27
F13506.S28
F13506.S29
F13506.S30
F13506.S31
F13506.S32
F13506.S33
F13506.S34
F13506.S35
F13506.S36
F13506.S37
F13506.S38
F13506.S39
F13506.S40
F13506.S41
F13506.S42
F13506.S43
F13506.S44
F13506.S45
F13506.S46
F13506.S47
F13506.S48
F13506.S49
F13506.S50
F13506.S51
F13506.S52
F13506.S53
F13506.S54
F13506.S55
F13506.S56
F13506.S57
F13506.S58
F13506.S59
F13506.S60
F13506.S61
F13506.S62
F13506.S63
F13506.S64
Row Sum
Percentage
input
169,607
123,569
120,234
117,006
123,477
110,818
140,890
132,673
83,657
218,741
115,796
83,081
112,520
141,394
87,218
171,466
127,919
110,730
103,016
73,142
153,260
130,572
160,012
78,143
108,678
118,557
149,831
109,423
98,838
90,808
113,749
132,651
131,869
72,081
131,639
129,360
73,309
75,479
182,065
113,774
71,829
121,763
80,174
87,005
85,702
71,150
122,919
116,276
71,742
115,837
146,040
161,267
107,524
116,000
188,153
119,820
103,476
88,054
85,722
91,325
120,958
126,817
109,679
133,087
7,463,371
100.00%
filtered
159,391
116,052
112,925
109,752
115,982
103,888
132,400
124,532
78,597
205,591
108,838
77,953
105,540
132,698
81,895
160,721
120,120
103,913
96,743
68,672
144,095
122,520
150,382
73,167
101,661
111,264
140,470
102,388
92,653
85,038
106,313
124,350
123,609
67,466
123,198
121,513
68,611
70,684
170,523
106,553
67,188
114,065
75,100
81,714
80,337
66,639
114,925
109,158
67,256
108,511
136,753
151,123
100,854
108,795
176,282
112,394
97,067
82,436
80,387
85,481
113,231
118,833
102,625
124,712
6,998,527
93.77%
denoisedF
158,454
115,761
112,582
109,582
115,405
103,354
132,152
124,262
78,477
205,124
108,616
77,682
105,256
132,290
81,797
160,252
119,674
103,572
96,518
68,417
143,554
122,279
149,466
72,243
100,251
110,734
138,683
100,309
90,766
83,703
104,990
120,778
122,637
66,177
120,138
121,146
67,225
69,506
167,248
104,776
65,610
111,865
73,397
80,005
78,618
64,697
113,171
108,995
65,808
106,819
133,837
147,623
98,583
107,389
174,016
110,868
95,430
80,821
79,046
83,872
111,559
116,240
100,914
121,782
6,916,801
92.68%
denoisedR
156,667
114,416
111,196
108,086
114,239
102,387
130,535
122,949
77,659
202,904
107,195
76,961
103,969
130,935
80,767
158,548
118,256
102,186
95,225
67,615
141,768
120,710
148,267
71,623
99,387
109,550
137,255
100,214
90,416
83,146
104,005
121,825
121,136
65,924
120,609
119,503
66,953
69,012
166,947
104,314
65,681
111,476
73,262
79,865
78,385
64,987
112,677
107,682
65,263
105,928
133,617
147,392
98,310
106,157
172,263
110,366
94,436
80,181
77,966
83,300
110,399
115,943
100,143
122,010
6,862,948
91.96%
merged
153,454
112,936
110,124
107,017
112,228
100,199
129,058
121,667
76,957
200,718
104,393
76,041
102,501
129,450
79,335
156,996
116,333
100,729
93,035
66,264
139,306
119,410
144,757
69,865
96,441
107,755
133,514
97,337
87,439
80,903
101,467
116,980
118,361
63,913
116,041
117,512
65,024
67,048
161,762
101,175
63,432
107,785
70,557
77,093
75,499
62,541
109,526
106,503
62,927
102,864
128,082
141,679
94,725
103,927
167,850
107,913
91,520
77,715
75,269
80,751
107,027
111,987
97,402
117,649
6,697,668
89.74%
nonchim
133,649
110,957
108,840
106,237
95,679
82,647
128,234
120,762
76,760
199,223
95,436
63,609
84,191
126,121
71,042
129,333
103,171
91,399
63,998
60,304
123,193
112,152
127,447
52,536
55,389
102,317
104,870
55,990
72,168
48,872
81,260
72,390
91,089
49,142
75,617
104,755
44,153
56,151
84,394
76,928
39,010
82,403
45,823
63,119
48,326
44,359
80,049
97,798
47,004
93,694
89,826
76,287
68,143
84,455
124,015
105,546
74,214
62,187
59,417
55,313
89,811
79,706
61,725
72,424
5,387,059
72.18%
This table can be downloaded as an Excel table below:
5. DADA2 Amplicon Sequence Variants (ASVs). A total of 6802 unique merged and chimera-free ASV sequences were identified, and their corresponding
read counts for each sample are available in the "ASV Read Count Table" with rows for the ASV sequences and columns for sample. This read count table can be used for
microbial profile comparison among different samples and the sequences provided in the table can be used to taxonomy assignment.
The species-level, open-reference 16S rRNA NGS reads taxonomy assignment pipeline
Version 20210310
1. Raw sequences reads in FASTA format were BLASTN-searched against a combined set of 16S rRNA reference sequences.
It consists of MOMD (version 0.1), the HOMD (version 15.2 http://www.homd.org/index.php?name=seqDownload&file&type=R ),
HOMD 16S rRNA RefSeq Extended Version 1.1 (EXT), GreenGene Gold (GG)
(http://greengenes.lbl.gov/Download/Sequence_Data/Fasta_data_files/gold_strains_gg16S_aligned.fasta.gz) ,
and the NCBI 16S rRNA reference sequence set (https://ftp.ncbi.nlm.nih.gov/blast/db/16S_ribosomal_RNA.tar.gz).
These sequences were screened and combined to remove short sequences (<1000nt), chimera, duplicated and sub-sequences,
as well as sequences with poor taxonomy annotation (e.g., without species information).
This process resulted in 1,015 from HOMD V15.22, 495 from EXT, 3,940 from GG and 18,044 from NCBI, a total of 25,120 sequences.
Altogether these sequence represent a total of 15,601 oral and non-oral microbial species.
The NCBI BLASTN version 2.7.1+ (Zhang et al, 2000) was used with the default parameters.
Reads with ≥ 98% sequence identity to the matched reference and ≥ 90% alignment length
(i.e., ≥ 90% of the read length that was aligned to the reference and was used to calculate
the sequence percent identity) were classified based on the taxonomy of the reference sequence
with highest sequence identity. If a read matched with reference sequences representing
more than one species with equal percent identity and alignment length, it was subject
to chimera checking with USEARCH program version v8.1.1861 (Edgar 2010). Non-chimeric reads with multi-species
best hits were considered valid and were assigned with a unique species
notation (e.g., spp) denoting unresolvable multiple species.
2. Unassigned reads (i.e., reads with < 98% identity or < 90% alignment length) were pooled together and reads < 200 bases were
removed. The remaining reads were subject to the de novo
operational taxonomy unit (OTU) calling and chimera checking using the USEARCH program version v8.1.1861 (Edgar 2010).
The de novo OTU calling and chimera checking was done using 98% as the sequence identity cutoff, i.e., the species-level OTU.
The output of this step produced species-level de novo clustered OTUs with 98% identity.
Representative reads from each of the OTUs/species were then BLASTN-searched
against the same reference sequence set again to determine the closest species for
these potential novel species. These potential novel species were pooled together with the reads that were signed to specie-level in
the previous step, for down-stream analyses.
Reference:
Edgar RC. Search and clustering orders of magnitude faster than BLAST.
Bioinformatics. 2010 Oct 1;26(19):2460-1. doi: 10.1093/bioinformatics/btq461. Epub 2010 Aug 12. PubMed PMID: 20709691.
3. Designations used in the taxonomy:
1) Taxonomy levels are indicated by these prefixes:
k__: domain/kingdom
p__: phylum
c__: class
o__: order
f__: family
g__: genus
s__: species
Example:
k__Bacteria;p__Firmicutes;c__Clostridia;o__Clostridiales;f__Lachnospiraceae;g__Blautia;s__faecis
2) Unique level identified – known species:
k__Bacteria;p__Firmicutes;c__Clostridia;o__Clostridiales;f__Lachnospiraceae;g__Roseburia;s__hominis
The above example shows some reads match to a single species (all levels are unique)
3) Non-unique level identified – known species:
k__Bacteria;p__Firmicutes;c__Clostridia;o__Clostridiales;f__Lachnospiraceae;g__Roseburia;s__multispecies_spp123_3
The above example “s__multispecies_spp123_3” indicates certain reads equally match to 3 species of the
genus Roseburia; the “spp123” is a temporally assigned species ID.
k__Bacteria;p__Firmicutes;c__Clostridia;o__Clostridiales;f__Lachnospiraceae;g__multigenus;s__multispecies_spp234_5
The above example indicates certain reads match equally to 5 different species, which belong to multiple genera.;
the “spp234” is a temporally assigned species ID.
4) Unique level identified – unknown species, potential novel species:
k__Bacteria;p__Firmicutes;c__Clostridia;o__Clostridiales;f__Lachnospiraceae;g__Roseburia;s__ hominis_nov_97%
The above example indicates that some reads have no match to any of the reference sequences with
sequence identity ≥ 98% and percent coverage (alignment length) ≥ 98% as well. However this groups
of reads (actually the representative read from a de novo OTU) has 96% percent identity to
Roseburia hominis, thus this is a potential novel species, closest to Roseburia hominis.
(But they are not the same species).
5) Multiple level identified – unknown species, potential novel species:
k__Bacteria;p__Firmicutes;c__Clostridia;o__Clostridiales;f__Lachnospiraceae;g__Roseburia;s__ multispecies_sppn123_3_nov_96%
The above example indicates that some reads have no match to any of the reference sequences
with sequence identity ≥ 98% and percent coverage (alignment length) ≥ 98% as well.
However this groups of reads (actually the representative read from a de novo OTU)
has 96% percent identity equally to 3 species in Roseburia. Thus this is no single
closest species, instead this group of reads match equally to multiple species at 96%.
Since they have passed chimera check so they represent a novel species. “sppn123” is a
temporary ID for this potential novel species.
4. The taxonomy assignment algorithm is illustrated in this flow char below:
Read Taxonomy Assignment - Result Summary *
Code
Category
MPC=0% (>=1 read)
MPC=0.01%(>=309 reads)
A
Total reads
5,387,059
5,387,059
B
Total assigned reads
3,091,006
3,091,006
C
Assigned reads in species with read count < MPC
0
10,458
D
Assigned reads in samples with read count < 500
0
0
E
Total samples
64
64
F
Samples with reads >= 500
64
64
G
Samples with reads < 500
0
0
H
Total assigned reads used for analysis (B-C-D)
3,091,006
3,080,548
I
Reads assigned to single species
2,315,489
2,308,931
J
Reads assigned to multiple species
675,081
673,801
K
Reads assigned to novel species
100,436
97,816
L
Total number of species
217
84
M
Number of single species
119
63
N
Number of multi-species
21
8
O
Number of novel species
77
13
P
Total unassigned reads
2,296,053
2,296,053
Q
Chimeric reads
135,777
135,777
R
Reads without BLASTN hits
1,367,381
1,367,381
S
Others: short, low quality, singletons, etc.
792,895
792,895
A=B+P=C+D+H+Q+R+S
E=F+G
B=C+D+H
H=I+J+K
L=M+N+O
P=Q+R+S
* MPC = Minimal percent (of all assigned reads) read count per species, species with read count < MPC were removed.
* Samples with reads < 500 were removed from downstream analyses.
* The assignment result from MPC=0.1% was used in the downstream analyses.
Read Taxonomy Assignment - ASV Species-Level Read Counts Table
This table shows the read counts for each sample (columns) and each species identified based on the ASV sequences.
The downstream analyses were based on this table.
The species listed in the table has full taxonomy and a dynamically assigned species ID specific to this report.
When some reads match with the reference sequences of more than one species equally (i.e., same percent identiy and alignmnet coverage),
they can't be assigned to a particular species. Instead, they are assigned to multiple species with the species notaton
"s__multispecies_spp2_2". In this notation, spp2 is the dynamic ID assigned to these reads that hit multiple sequences and the "_2"
at the end of the notation means there are two species in the spp2.
You can look up which species are included in the multi-species assignment, in this table below:
Another type of notation is "s__multispecies_sppn2_2", in which the "n" in the sppn2 means it's a potential novel species because all the reads in this species
have < 98% idenity to any of the reference sequences. They were grouped together based on de novo OTU clustering at 98% identity cutoff. And then
a representative sequence was chosed to BLASTN search against the reference database to find the closest match (but will still be < 98%). This representative
sequence also matched equally to more than one species, hence the "spp" was given in the label.
In ecology, alpha diversity (α-diversity) is the mean species diversity in sites or habitats at a local scale.
The term was introduced by R. H. Whittaker[1][2] together with the terms beta diversity (β-diversity)
and gamma diversity (γ-diversity). Whittaker's idea was that the total species diversity in a landscape
(gamma diversity) is determined by two different things, the mean species diversity in sites or habitats
at a more local scale (alpha diversity) and the differentiation among those habitats (beta diversity).
Diversity measures are affected by the sampling depth. Rarefaction is a technique to assess species richness from the results of sampling. Rarefaction allows
the calculation of species richness for a given number of individual samples, based on the construction
of so-called rarefaction curves. This curve is a plot of the number of species as a function of the
number of samples. Rarefaction curves generally grow rapidly at first, as the most common species are found,
but the curves plateau as only the rarest species remain to be sampled.
The two main factors taken into account when measuring diversity are richness and evenness.
Richness is a measure of the number of different kinds of organisms present in a particular area.
Evenness compares the similarity of the population size of each of the species present. There are
many different ways to measure the richness and evenness. These measurements are called "estimators" or "indices".
Below is a diversity of 3 commonly used indices showing the values for all the samples (dots) and in groups (boxes).
Alpha Diversity Box Plots for All Groups
Alpha Diversity Box Plots for Individual Comparisons
To test whether the alpha diversity among different comparison groups are different statistically, we use the Kruskal Wallis H test
provided the "alpha-group-significance" fucntion in the QIIME 2 "diversity" package. Kruskal Wallis H test is the non-parametric alternative
to the One Way ANOVA. Non-parametric means that the test doesn’t assume your data comes from a particular distribution. The H test is used
when the assumptions for ANOVA aren’t met (like the assumption of normality). It is sometimes called the one-way ANOVA on ranks,
as the ranks of the data values are used in the test rather than the actual data points. The H test determines whether the medians of two
or more groups are different.
Below are the Kruskal Wallis H test results for each comparison based on three different alpha diversity measures: 1) Observed species (features),
2) Shannon index, and 3) Simpson index.
Beta diversity compares the similarity (or dissimilarity) of microbial profiles between different
groups of samples. There are many different similarity/dissimilarity metrics.
In general, they can be quantitative (using sequence abundance, e.g., Bray-Curtis or weighted UniFrac)
or binary (considering only presence-absence of sequences, e.g., binary Jaccard or unweighted UniFrac).
They can be even based on phylogeny (e.g., UniFrac metrics) or not (non-UniFrac metrics, such as Bray-Curtis, etc.).
For microbiome studies, species profiles of samples can be compared with the Bray-Curtis dissimilarity,
which is based on the count data type. The pair-wise Bray-Curtis dissimilarity matrix of all samples can then be
subject to either multi-dimensional scaling (MDS, also known as PCoA) or non-metric MDS (NMDS).
MDS/PCoA is a
scaling or ordination method that starts with a matrix of similarities or dissimilarities
between a set of samples and aims to produce a low-dimensional graphical plot of the data
in such a way that distances between points in the plot are close to original dissimilarities.
NMDS is similar to MDS, however it does not use the dissimilarities data, instead it converts them into
the ranks and use these ranks in the calculation.
In our beta diversity analysis, Bray-Curtis dissimilarity matrix was first calculated and then plotted by the PCoA and
NMDS separately. Below are beta diveristy results for all groups together:
NMDS and PCoA Plots for All Groups
The above PCoA and NMDS plots are based on count data. The count data can also be transformed into centered log ratio (CLR)
for each species. The CLR data is no longer count data and cannot be used in Bray-Curtis dissimilarity calculation. Instead
CLR can be compared with Euclidean distances. When CLR data are compared by Euclidean distance, the distance is also called
Aitchison distance.
Below are the NMDS and PCoA plots of the Aitchison distances of the samples:
Interactive 3D PCoA Plots - Bray-Curtis Dissimilarity
Interactive 3D PCoA Plots - Euclidean Distance
Interactive 3D PCoA Plots - Correlation Coefficients
Group Significance of Beta-diversity Indices
To test whether the between-group dissimilarities are significantly greater than the within-group dissimilarities,
the "beta-group-significance" function provided in the QIIME 2 "diversity" package was used with PERMANOVA
(permutational multivariate analysis of variance) as the group significant testing method.
Three beta diversity matrics were used: 1) Bray–Curtis dissimilarity 2) Correlation coefficient matrix , and 3) Aitchison distance
(Euclidean distance between clr-transformed compositions).
16S rRNA next generation sequencing (NGS) generates a fixed number of reads that reflect the proportion of different
species in a sample, i.e., the relative abundance of species, instead of the absolute abundance.
In Mathematics, measurements involving probabilities, proportions, percentages, and ppm can all
be thought of as compositional data. This makes the microbiome read count data “compositional”
(Gloor et al, 2017). In general, compositional data represent parts of a whole which only
carry relative information (http://www.compositionaldata.com/).
The problem of microbiome data being compositional arises when comparing two groups of samples for
identifying “differentially abundant” species. A species with the same absolute abundance between two
conditions, its relative abundances in the two conditions (e.g., percent abundance) can become different
if the relative abundance of other species change greatly. This problem can lead to incorrect conclusion
in terms of differential abundance for microbial species in the samples.
When studying differential abundance (DA), the current better approach is to transform the read count
data into log ratio data. The ratios are calculated between read counts of all species in a sample to
a “reference” count (e.g., mean read count of the sample). The log ratio data allow the detection of DA
species without being affected by percentage bias mentioned above
In this report, a compositional DA analysis tool “ANCOM” (analysis of composition of microbiomes)
was used. ANCOM transforms the count data into log-ratios and thus is more suitable for comparing
the composition of microbiomes in two or more populations. "ANCOM" generates a table of features with
W-statistics and whether the null hypothesis is rejected. The “W” is the W-statistic, or number of
features that a single feature is tested to be significantly different against. Hence the higher the "W"
the more statistical sifgnificant that a feature/species is differentially abundant.
References:
Gloor GB, Macklaim JM, Pawlowsky-Glahn V, Egozcue JJ. Microbiome Datasets Are Compositional: And This Is Not Optional. Front Microbiol.
2017 Nov 15;8:2224. doi: 10.3389/fmicb.2017.02224. PMID: 29187837; PMCID: PMC5695134.
Mandal S, Van Treuren W, White RA, Eggesbø M, Knight R, Peddada SD. Analysis of composition of
microbiomes: a novel method for studying microbial composition. Microb Ecol Health Dis.
2015 May 29;26:27663. doi: 10.3402/mehd.v26.27663. PMID: 26028277; PMCID: PMC4450248.
Lin H, Peddada SD. Analysis of compositions of microbiomes with bias correction.
Nat Commun. 2020 Jul 14;11(1):3514. doi: 10.1038/s41467-020-17041-7.
PMID: 32665548; PMCID: PMC7360769.
Starting with version V1.2, we include the results of ANCOM-BC (Analysis of Compositions of
Microbiomes with Bias Correction) (Lin and Peddada 2020). ANCOM-BC is an updated version of "ANCOM" that:
(a) provides statistically valid test with appropriate p-values,
(b) provides confidence intervals for differential abundance of each taxon,
(c) controls the False Discovery Rate (FDR),
(d) maintains adequate power, and
(e) is computationally simple to implement.
The bias correction (BC) addresses a challenging problem of the bias introduced by differences in
the sampling fractions across samples. This bias has been a major hurdle in performing DA analysis of microbiome data.
ANCOM-BC estimates the unknown sampling fractions and corrects the bias induced by their differences among samples.
The absolute abundance data are modeled using a linear regression framework.
Starting with version V1.43, ANCOM-BC2 is used instead of ANCOM-BC, So that multiple pairwise directional test can be performed (if there are more than two gorups in a comparison).
When performing pairwise directional test, the mixed directional false discover rate (mdFDR) is taken into account. The mdFDR
is the combination of false discovery rate due to multiple testing, multiple pairwise comparisons, and directional tests within
each pairwise comparison. The mdFDR is adopted from (Guo, Sarkar, and Peddada 2010; Grandhi, Guo, and Peddada 2016). For more detail
explanation and additional features of ANCOM-BC2 please see author's documentation.
References:
Lin H, Peddada SD. Analysis of compositions of microbiomes with bias correction.
Nat Commun. 2020 Jul 14;11(1):3514. doi: 10.1038/s41467-020-17041-7.
PMID: 32665548; PMCID: PMC7360769.
Guo W, Sarkar SK, Peddada SD. Controlling false discoveries in multidimensional directional decisions, with applications to gene expression data on ordered categories. Biometrics. 2010 Jun;66(2):485-92. doi: 10.1111/j.1541-0420.2009.01292.x. Epub 2009 Jul 23. PMID: 19645703; PMCID: PMC2895927.
Grandhi A, Guo W, Peddada SD. A multiple testing procedure for multi-dimensional pairwise comparisons with application to gene expression studies. BMC Bioinformatics. 2016 Feb 25;17:104. doi: 10.1186/s12859-016-0937-5. PMID: 26917217; PMCID: PMC4768411.
LEfSe (Linear Discriminant Analysis Effect Size) is an alternative method to find "organisms, genes, or
pathways that consistently explain the differences between two or more microbial communities" (Segata et al., 2011).
Specifically, LEfSe uses rank-based Kruskal-Wallis (KW) sum-rank test to detect features with significant
differential (relative) abundance with respect to the class of interest. Since it is rank-based, instead of proportional based,
the differential species identified among the comparison groups is less biased (than percent abundance based).
Reference:
Segata N, Izard J, Waldron L, Gevers D, Miropolsky L, Garrett WS, Huttenhower C. Metagenomic biomarker discovery and explanation. Genome Biol. 2011 Jun 24;12(6):R60. doi: 10.1186/gb-2011-12-6-r60. PMID: 21702898; PMCID: PMC3218848.
To analyze the co-occurrence or co-exclusion between microbial species among different samples, network correlation
analysis tools are usually used for this purpose. However, microbiome count data are compositional. If count data are normalized to the total number of counts in the
sample, the data become not independent and traditional statistical metrics (e.g., correlation) for the detection
of specie-species relationships can lead to spurious results. In addition, sequencing-based studies typically
measure hundreds of OTUs (species) on few samples; thus, inference of OTU-OTU association networks is severely
under-powered. Here we use SPIEC-EASI (SParse InversECovariance Estimation
for Ecological Association Inference), a statistical method for the inference of microbial
ecological networks from amplicon sequencing datasets that addresses both of these issues (Kurtz et al., 2015).
SPIEC-EASI combines data transformations developed for compositional data analysis with a graphical model
inference framework that assumes the underlying ecological association network is sparse. SPIEC-EASI provides
two algorithms for network inferencing – 1) Meinshausen-Bühlmann's neighborhood selection (MB method) and inverse covariance selection
(GLASSO method, i.e., graphical least absolute shrinkage and selection operator). This is fundamentally distinct from SparCC, which essentially estimate pairwise correlations. In addition
to these two methods, we provide the results of a third method - SparCC (Sparse Correlations for Compositional Data)(Friedman & Alm 2012), which
is also a method for inferring correlations from compositional data. SparCC estimates the linear Pearson correlations between
the log-transformed components.
References:
Kurtz ZD, Müller CL, Miraldi ER, Littman DR, Blaser MJ, Bonneau RA. Sparse and compositionally robust inference of microbial ecological networks. PLoS Comput Biol. 2015 May 7;11(5):e1004226. doi: 10.1371/journal.pcbi.1004226. PMID: 25950956; PMCID: PMC4423992.
The results of this analysis are for research purpose only. They are not intended to diagnose, treat, cure, or prevent any disease. Forsyth and FOMC
are not responsible for use of information provided in this report outside the research area.
