Project FOMC4401_9929_13506_15267 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, the following DNA
extraction kit was used according to the manufacturer’s instructions:
☑
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)
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® NextSeq 2000™ with a p1
(Illumina, Sand Diego, CA) reagent kit (600 cycles). The sequencing was performed
with 25% 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 Pac-Bio full-length (V1V9) 16S rRNA amplicon sequencing, raw sequences are available for download in a single compressed zip file in the download link below.
After unzipping, you will find individual sequence files for each of your samples with the file extension “*.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 fastq files are listed in the table below:
Sample ID
Original Sample ID
Read 1 File Name
Read 2 File Name
F4401.S01
zr4401_10V1V3_R1.fastq.gz
zr4401_10V1V3_R2.fastq.gz
F4401.S02
zr4401_11V1V3_R1.fastq.gz
zr4401_11V1V3_R2.fastq.gz
F4401.S03
zr4401_12V1V3_R1.fastq.gz
zr4401_12V1V3_R2.fastq.gz
F4401.S04
zr4401_13V1V3_R1.fastq.gz
zr4401_13V1V3_R2.fastq.gz
F4401.S05
zr4401_14V1V3_R1.fastq.gz
zr4401_14V1V3_R2.fastq.gz
F4401.S06
zr4401_15V1V3_R1.fastq.gz
zr4401_15V1V3_R2.fastq.gz
F4401.S11
zr4401_16V1V3_R1.fastq.gz
zr4401_16V1V3_R2.fastq.gz
F4401.S08
zr4401_17V1V3_R1.fastq.gz
zr4401_17V1V3_R2.fastq.gz
F4401.S09
zr4401_18V1V3_R1.fastq.gz
zr4401_18V1V3_R2.fastq.gz
F4401.S10
zr4401_19V1V3_R1.fastq.gz
zr4401_19V1V3_R2.fastq.gz
F4401.S07
zr4401_1V1V3_R1.fastq.gz
zr4401_1V1V3_R2.fastq.gz
F4401.S12
zr4401_20V1V3_R1.fastq.gz
zr4401_20V1V3_R2.fastq.gz
F4401.S13
zr4401_21V1V3_R1.fastq.gz
zr4401_21V1V3_R2.fastq.gz
F4401.S14
zr4401_22V1V3_R1.fastq.gz
zr4401_22V1V3_R2.fastq.gz
F4401.S16
zr4401_24V1V3_R1.fastq.gz
zr4401_24V1V3_R2.fastq.gz
F4401.S17
zr4401_25V1V3_R1.fastq.gz
zr4401_25V1V3_R2.fastq.gz
F4401.S18
zr4401_26V1V3_R1.fastq.gz
zr4401_26V1V3_R2.fastq.gz
F4401.S19
zr4401_27V1V3_R1.fastq.gz
zr4401_27V1V3_R2.fastq.gz
F4401.S20
zr4401_28V1V3_R1.fastq.gz
zr4401_28V1V3_R2.fastq.gz
F4401.S21
zr4401_29V1V3_R1.fastq.gz
zr4401_29V1V3_R2.fastq.gz
F4401.S22
zr4401_2V1V3_R1.fastq.gz
zr4401_2V1V3_R2.fastq.gz
F4401.S23
zr4401_30V1V3_R1.fastq.gz
zr4401_30V1V3_R2.fastq.gz
F4401.S24
zr4401_31V1V3_R1.fastq.gz
zr4401_31V1V3_R2.fastq.gz
F4401.S25
zr4401_32V1V3_R1.fastq.gz
zr4401_32V1V3_R2.fastq.gz
F4401.S26
zr4401_33V1V3_R1.fastq.gz
zr4401_33V1V3_R2.fastq.gz
F4401.S27
zr4401_34V1V3_R1.fastq.gz
zr4401_34V1V3_R2.fastq.gz
F4401.S28
zr4401_35V1V3_R1.fastq.gz
zr4401_35V1V3_R2.fastq.gz
F4401.S29
zr4401_36V1V3_R1.fastq.gz
zr4401_36V1V3_R2.fastq.gz
F4401.S30
zr4401_37V1V3_R1.fastq.gz
zr4401_37V1V3_R2.fastq.gz
F4401.S31
zr4401_38V1V3_R1.fastq.gz
zr4401_38V1V3_R2.fastq.gz
F4401.S32
zr4401_39V1V3_R1.fastq.gz
zr4401_39V1V3_R2.fastq.gz
F4401.S33
zr4401_3V1V3_R1.fastq.gz
zr4401_3V1V3_R2.fastq.gz
F4401.S34
zr4401_40V1V3_R1.fastq.gz
zr4401_40V1V3_R2.fastq.gz
F4401.S35
zr4401_41V1V3_R1.fastq.gz
zr4401_41V1V3_R2.fastq.gz
F4401.S36
zr4401_42V1V3_R1.fastq.gz
zr4401_42V1V3_R2.fastq.gz
F4401.S37
zr4401_43V1V3_R1.fastq.gz
zr4401_43V1V3_R2.fastq.gz
F4401.S38
zr4401_44V1V3_R1.fastq.gz
zr4401_44V1V3_R2.fastq.gz
F4401.S39
zr4401_45V1V3_R1.fastq.gz
zr4401_45V1V3_R2.fastq.gz
F4401.S40
zr4401_46V1V3_R1.fastq.gz
zr4401_46V1V3_R2.fastq.gz
F4401.S41
zr4401_47V1V3_R1.fastq.gz
zr4401_47V1V3_R2.fastq.gz
F4401.S42
zr4401_4V1V3_R1.fastq.gz
zr4401_4V1V3_R2.fastq.gz
F4401.S43
zr4401_5V1V3_R1.fastq.gz
zr4401_5V1V3_R2.fastq.gz
F4401.S44
zr4401_6V1V3_R1.fastq.gz
zr4401_6V1V3_R2.fastq.gz
F4401.S45
zr4401_7V1V3_R1.fastq.gz
zr4401_7V1V3_R2.fastq.gz
F4401.S46
zr4401_8V1V3_R1.fastq.gz
zr4401_8V1V3_R2.fastq.gz
F4401.S47
zr4401_9V1V3_R1.fastq.gz
zr4401_9V1V3_R2.fastq.gz
F9929.S10
zr9929_10V1V3_R1.fastq.gz
zr9929_10V1V3_R2.fastq.gz
F9929.S11
zr9929_11V1V3_R1.fastq.gz
zr9929_11V1V3_R2.fastq.gz
F9929.S12
zr9929_12V1V3_R1.fastq.gz
zr9929_12V1V3_R2.fastq.gz
F9929.S13
zr9929_13V1V3_R1.fastq.gz
zr9929_13V1V3_R2.fastq.gz
F9929.S14
zr9929_14V1V3_R1.fastq.gz
zr9929_14V1V3_R2.fastq.gz
F9929.S15
zr9929_15V1V3_R1.fastq.gz
zr9929_15V1V3_R2.fastq.gz
F9929.S16
zr9929_16V1V3_R1.fastq.gz
zr9929_16V1V3_R2.fastq.gz
F9929.S17
zr9929_17V1V3_R1.fastq.gz
zr9929_17V1V3_R2.fastq.gz
F9929.S18
zr9929_18V1V3_R1.fastq.gz
zr9929_18V1V3_R2.fastq.gz
F9929.S19
zr9929_19V1V3_R1.fastq.gz
zr9929_19V1V3_R2.fastq.gz
F9929.S01
zr9929_1V1V3_R1.fastq.gz
zr9929_1V1V3_R2.fastq.gz
F9929.S20
zr9929_20V1V3_R1.fastq.gz
zr9929_20V1V3_R2.fastq.gz
F9929.S21
zr9929_21V1V3_R1.fastq.gz
zr9929_21V1V3_R2.fastq.gz
F9929.S22
zr9929_22V1V3_R1.fastq.gz
zr9929_22V1V3_R2.fastq.gz
F9929.S23
zr9929_23V1V3_R1.fastq.gz
zr9929_23V1V3_R2.fastq.gz
F9929.S24
zr9929_24V1V3_R1.fastq.gz
zr9929_24V1V3_R2.fastq.gz
F9929.S25
zr9929_25V1V3_R1.fastq.gz
zr9929_25V1V3_R2.fastq.gz
F9929.S26
zr9929_26V1V3_R1.fastq.gz
zr9929_26V1V3_R2.fastq.gz
F9929.S27
zr9929_27V1V3_R1.fastq.gz
zr9929_27V1V3_R2.fastq.gz
F9929.S28
zr9929_28V1V3_R1.fastq.gz
zr9929_28V1V3_R2.fastq.gz
F9929.S29
zr9929_29V1V3_R1.fastq.gz
zr9929_29V1V3_R2.fastq.gz
F9929.S02
zr9929_2V1V3_R1.fastq.gz
zr9929_2V1V3_R2.fastq.gz
F9929.S30
zr9929_30V1V3_R1.fastq.gz
zr9929_30V1V3_R2.fastq.gz
F9929.S31
zr9929_31V1V3_R1.fastq.gz
zr9929_31V1V3_R2.fastq.gz
F9929.S32
zr9929_32V1V3_R1.fastq.gz
zr9929_32V1V3_R2.fastq.gz
F9929.S33
zr9929_33V1V3_R1.fastq.gz
zr9929_33V1V3_R2.fastq.gz
F9929.S34
zr9929_34V1V3_R1.fastq.gz
zr9929_34V1V3_R2.fastq.gz
F9929.S35
zr9929_35V1V3_R1.fastq.gz
zr9929_35V1V3_R2.fastq.gz
F9929.S03
zr9929_3V1V3_R1.fastq.gz
zr9929_3V1V3_R2.fastq.gz
F9929.S04
zr9929_4V1V3_R1.fastq.gz
zr9929_4V1V3_R2.fastq.gz
F9929.S05
zr9929_5V1V3_R1.fastq.gz
zr9929_5V1V3_R2.fastq.gz
F9929.S06
zr9929_6V1V3_R1.fastq.gz
zr9929_6V1V3_R2.fastq.gz
F9929.S07
zr9929_7V1V3_R1.fastq.gz
zr9929_7V1V3_R2.fastq.gz
F9929.S08
zr9929_8V1V3_R1.fastq.gz
zr9929_8V1V3_R2.fastq.gz
F9929.S09
zr9929_9V1V3_R1.fastq.gz
zr9929_9V1V3_R2.fastq.gz
F15267.S10
zr15267_10V1V3_R1.fastq.gz
zr15267_10V1V3_R2.fastq.gz
F15267.S11
zr15267_11V1V3_R1.fastq.gz
zr15267_11V1V3_R2.fastq.gz
F15267.S12
zr15267_12V1V3_R1.fastq.gz
zr15267_12V1V3_R2.fastq.gz
F15267.S13
zr15267_13V1V3_R1.fastq.gz
zr15267_13V1V3_R2.fastq.gz
F15267.S14
zr15267_14V1V3_R1.fastq.gz
zr15267_14V1V3_R2.fastq.gz
F15267.S15
zr15267_15V1V3_R1.fastq.gz
zr15267_15V1V3_R2.fastq.gz
F15267.S16
zr15267_16V1V3_R1.fastq.gz
zr15267_16V1V3_R2.fastq.gz
F15267.S17
zr15267_17V1V3_R1.fastq.gz
zr15267_17V1V3_R2.fastq.gz
F15267.S18
zr15267_18V1V3_R1.fastq.gz
zr15267_18V1V3_R2.fastq.gz
F15267.S19
zr15267_19V1V3_R1.fastq.gz
zr15267_19V1V3_R2.fastq.gz
F15267.S01
zr15267_1V1V3_R1.fastq.gz
zr15267_1V1V3_R2.fastq.gz
F15267.S20
zr15267_20V1V3_R1.fastq.gz
zr15267_20V1V3_R2.fastq.gz
F15267.S21
zr15267_21V1V3_R1.fastq.gz
zr15267_21V1V3_R2.fastq.gz
F15267.S22
zr15267_22V1V3_R1.fastq.gz
zr15267_22V1V3_R2.fastq.gz
F15267.S23
zr15267_23V1V3_R1.fastq.gz
zr15267_23V1V3_R2.fastq.gz
F15267.S24
zr15267_24V1V3_R1.fastq.gz
zr15267_24V1V3_R2.fastq.gz
F15267.S25
zr15267_25V1V3_R1.fastq.gz
zr15267_25V1V3_R2.fastq.gz
F15267.S26
zr15267_26V1V3_R1.fastq.gz
zr15267_26V1V3_R2.fastq.gz
F15267.S27
zr15267_27V1V3_R1.fastq.gz
zr15267_27V1V3_R2.fastq.gz
F15267.S28
zr15267_28V1V3_R1.fastq.gz
zr15267_28V1V3_R2.fastq.gz
F15267.S29
zr15267_29V1V3_R1.fastq.gz
zr15267_29V1V3_R2.fastq.gz
F15267.S02
zr15267_2V1V3_R1.fastq.gz
zr15267_2V1V3_R2.fastq.gz
F15267.S30
zr15267_30V1V3_R1.fastq.gz
zr15267_30V1V3_R2.fastq.gz
F15267.S31
zr15267_31V1V3_R1.fastq.gz
zr15267_31V1V3_R2.fastq.gz
F15267.S32
zr15267_32V1V3_R1.fastq.gz
zr15267_32V1V3_R2.fastq.gz
F15267.S33
zr15267_33V1V3_R1.fastq.gz
zr15267_33V1V3_R2.fastq.gz
F15267.S34
zr15267_34V1V3_R1.fastq.gz
zr15267_34V1V3_R2.fastq.gz
F15267.S35
zr15267_35V1V3_R1.fastq.gz
zr15267_35V1V3_R2.fastq.gz
F15267.S36
zr15267_36V1V3_R1.fastq.gz
zr15267_36V1V3_R2.fastq.gz
F15267.S37
zr15267_37V1V3_R1.fastq.gz
zr15267_37V1V3_R2.fastq.gz
F15267.S38
zr15267_38V1V3_R1.fastq.gz
zr15267_38V1V3_R2.fastq.gz
F15267.S39
zr15267_39V1V3_R1.fastq.gz
zr15267_39V1V3_R2.fastq.gz
F15267.S03
zr15267_3V1V3_R1.fastq.gz
zr15267_3V1V3_R2.fastq.gz
F15267.S40
zr15267_40V1V3_R1.fastq.gz
zr15267_40V1V3_R2.fastq.gz
F15267.S41
zr15267_41V1V3_R1.fastq.gz
zr15267_41V1V3_R2.fastq.gz
F15267.S42
zr15267_42V1V3_R1.fastq.gz
zr15267_42V1V3_R2.fastq.gz
F15267.S43
zr15267_43V1V3_R1.fastq.gz
zr15267_43V1V3_R2.fastq.gz
F15267.S44
zr15267_44V1V3_R1.fastq.gz
zr15267_44V1V3_R2.fastq.gz
F15267.S45
zr15267_45V1V3_R1.fastq.gz
zr15267_45V1V3_R2.fastq.gz
F15267.S46
zr15267_46V1V3_R1.fastq.gz
zr15267_46V1V3_R2.fastq.gz
F15267.S47
zr15267_47V1V3_R1.fastq.gz
zr15267_47V1V3_R2.fastq.gz
F15267.S48
zr15267_48V1V3_R1.fastq.gz
zr15267_48V1V3_R2.fastq.gz
F15267.S04
zr15267_4V1V3_R1.fastq.gz
zr15267_4V1V3_R2.fastq.gz
F15267.S05
zr15267_5V1V3_R1.fastq.gz
zr15267_5V1V3_R2.fastq.gz
F15267.S06
zr15267_6V1V3_R1.fastq.gz
zr15267_6V1V3_R2.fastq.gz
F15267.S07
zr15267_7V1V3_R1.fastq.gz
zr15267_7V1V3_R2.fastq.gz
F15267.S08
zr15267_8V1V3_R1.fastq.gz
zr15267_8V1V3_R2.fastq.gz
F15267.S09
zr15267_9V1V3_R1.fastq.gz
zr15267_9V1V3_R2.fastq.gz
F13506.S10
zr13506_10V1V3_R1.fastq.gz
zr13506_10V1V3_R2.fastq.gz
F13506.S11
zr13506_11V1V3_R1.fastq.gz
zr13506_11V1V3_R2.fastq.gz
F13506.S12
zr13506_12V1V3_R1.fastq.gz
zr13506_12V1V3_R2.fastq.gz
F13506.S13
zr13506_13V1V3_R1.fastq.gz
zr13506_13V1V3_R2.fastq.gz
F13506.S14
zr13506_14V1V3_R1.fastq.gz
zr13506_14V1V3_R2.fastq.gz
F13506.S15
zr13506_15V1V3_R1.fastq.gz
zr13506_15V1V3_R2.fastq.gz
F13506.S16
zr13506_16V1V3_R1.fastq.gz
zr13506_16V1V3_R2.fastq.gz
F13506.S17
zr13506_17V1V3_R1.fastq.gz
zr13506_17V1V3_R2.fastq.gz
F13506.S18
zr13506_18V1V3_R1.fastq.gz
zr13506_18V1V3_R2.fastq.gz
F13506.S19
zr13506_19V1V3_R1.fastq.gz
zr13506_19V1V3_R2.fastq.gz
F13506.S01
zr13506_1V1V3_R1.fastq.gz
zr13506_1V1V3_R2.fastq.gz
F13506.S20
zr13506_20V1V3_R1.fastq.gz
zr13506_20V1V3_R2.fastq.gz
F13506.S21
zr13506_21V1V3_R1.fastq.gz
zr13506_21V1V3_R2.fastq.gz
F13506.S22
zr13506_22V1V3_R1.fastq.gz
zr13506_22V1V3_R2.fastq.gz
F13506.S23
zr13506_23V1V3_R1.fastq.gz
zr13506_23V1V3_R2.fastq.gz
F13506.S24
zr13506_24V1V3_R1.fastq.gz
zr13506_24V1V3_R2.fastq.gz
F13506.S25
zr13506_25V1V3_R1.fastq.gz
zr13506_25V1V3_R2.fastq.gz
F13506.S26
zr13506_26V1V3_R1.fastq.gz
zr13506_26V1V3_R2.fastq.gz
F13506.S27
zr13506_27V1V3_R1.fastq.gz
zr13506_27V1V3_R2.fastq.gz
F13506.S28
zr13506_28V1V3_R1.fastq.gz
zr13506_28V1V3_R2.fastq.gz
F13506.S29
zr13506_29V1V3_R1.fastq.gz
zr13506_29V1V3_R2.fastq.gz
F13506.S02
zr13506_2V1V3_R1.fastq.gz
zr13506_2V1V3_R2.fastq.gz
F13506.S30
zr13506_30V1V3_R1.fastq.gz
zr13506_30V1V3_R2.fastq.gz
F13506.S31
zr13506_31V1V3_R1.fastq.gz
zr13506_31V1V3_R2.fastq.gz
F13506.S32
zr13506_32V1V3_R1.fastq.gz
zr13506_32V1V3_R2.fastq.gz
F13506.S33
zr13506_33V1V3_R1.fastq.gz
zr13506_33V1V3_R2.fastq.gz
F13506.S34
zr13506_34V1V3_R1.fastq.gz
zr13506_34V1V3_R2.fastq.gz
F13506.S35
zr13506_35V1V3_R1.fastq.gz
zr13506_35V1V3_R2.fastq.gz
F13506.S36
zr13506_36V1V3_R1.fastq.gz
zr13506_36V1V3_R2.fastq.gz
F13506.S37
zr13506_37V1V3_R1.fastq.gz
zr13506_37V1V3_R2.fastq.gz
F13506.S38
zr13506_38V1V3_R1.fastq.gz
zr13506_38V1V3_R2.fastq.gz
F13506.S39
zr13506_39V1V3_R1.fastq.gz
zr13506_39V1V3_R2.fastq.gz
F13506.S03
zr13506_3V1V3_R1.fastq.gz
zr13506_3V1V3_R2.fastq.gz
F13506.S40
zr13506_40V1V3_R1.fastq.gz
zr13506_40V1V3_R2.fastq.gz
F13506.S41
zr13506_41V1V3_R1.fastq.gz
zr13506_41V1V3_R2.fastq.gz
F13506.S42
zr13506_42V1V3_R1.fastq.gz
zr13506_42V1V3_R2.fastq.gz
F13506.S43
zr13506_43V1V3_R1.fastq.gz
zr13506_43V1V3_R2.fastq.gz
F13506.S44
zr13506_44V1V3_R1.fastq.gz
zr13506_44V1V3_R2.fastq.gz
F13506.S45
zr13506_45V1V3_R1.fastq.gz
zr13506_45V1V3_R2.fastq.gz
F13506.S46
zr13506_46V1V3_R1.fastq.gz
zr13506_46V1V3_R2.fastq.gz
F13506.S47
zr13506_47V1V3_R1.fastq.gz
zr13506_47V1V3_R2.fastq.gz
F13506.S48
zr13506_48V1V3_R1.fastq.gz
zr13506_48V1V3_R2.fastq.gz
F13506.S49
zr13506_49V1V3_R1.fastq.gz
zr13506_49V1V3_R2.fastq.gz
F13506.S04
zr13506_4V1V3_R1.fastq.gz
zr13506_4V1V3_R2.fastq.gz
F13506.S50
zr13506_50V1V3_R1.fastq.gz
zr13506_50V1V3_R2.fastq.gz
F13506.S51
zr13506_51V1V3_R1.fastq.gz
zr13506_51V1V3_R2.fastq.gz
F13506.S52
zr13506_52V1V3_R1.fastq.gz
zr13506_52V1V3_R2.fastq.gz
F13506.S53
zr13506_53V1V3_R1.fastq.gz
zr13506_53V1V3_R2.fastq.gz
F13506.S54
zr13506_54V1V3_R1.fastq.gz
zr13506_54V1V3_R2.fastq.gz
F13506.S55
zr13506_55V1V3_R1.fastq.gz
zr13506_55V1V3_R2.fastq.gz
F13506.S56
zr13506_56V1V3_R1.fastq.gz
zr13506_56V1V3_R2.fastq.gz
F13506.S57
zr13506_57V1V3_R1.fastq.gz
zr13506_57V1V3_R2.fastq.gz
F13506.S58
zr13506_58V1V3_R1.fastq.gz
zr13506_58V1V3_R2.fastq.gz
F13506.S59
zr13506_59V1V3_R1.fastq.gz
zr13506_59V1V3_R2.fastq.gz
F13506.S05
zr13506_5V1V3_R1.fastq.gz
zr13506_5V1V3_R2.fastq.gz
F13506.S60
zr13506_60V1V3_R1.fastq.gz
zr13506_60V1V3_R2.fastq.gz
F13506.S61
zr13506_61V1V3_R1.fastq.gz
zr13506_61V1V3_R2.fastq.gz
F13506.S62
zr13506_62V1V3_R1.fastq.gz
zr13506_62V1V3_R2.fastq.gz
F13506.S63
zr13506_63V1V3_R1.fastq.gz
zr13506_63V1V3_R2.fastq.gz
F13506.S64
zr13506_64V1V3_R1.fastq.gz
zr13506_64V1V3_R2.fastq.gz
F13506.S06
zr13506_6V1V3_R1.fastq.gz
zr13506_6V1V3_R2.fastq.gz
F13506.S07
zr13506_7V1V3_R1.fastq.gz
zr13506_7V1V3_R2.fastq.gz
F13506.S08
zr13506_8V1V3_R1.fastq.gz
zr13506_8V1V3_R2.fastq.gz
F13506.S09
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 [1].
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.
Callahan BJ, McMurdie PJ, Rosen MJ, Han AW, Johnson AJ, Holmes SP. DADA2: High-resolution sample inference from Illumina amplicon data. Nat Methods. 2016 Jul;13(7):581-3. doi: 10.1038/nmeth.3869. Epub 2016 May 23. PMID: 27214047; PMCID: PMC4927377.
Analysis Procedures:
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
77.09%
77.18%
77.37%
77.23%
77.17%
65.31%
311
77.17%
77.27%
77.26%
77.19%
65.57%
60.68%
301
77.49%
77.40%
77.46%
65.85%
61.14%
23.50%
291
77.62%
77.59%
66.10%
61.45%
23.90%
22.86%
281
76.68%
65.06%
60.52%
22.95%
22.09%
18.03%
271
64.34%
59.68%
22.26%
21.35%
17.31%
16.66%
Based on the above result, the trim length combination of R1 = 291 bases and R2 = 281 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
F15267.S01
F15267.S02
F15267.S03
F15267.S04
F15267.S05
F15267.S06
F15267.S07
F15267.S08
F15267.S09
F15267.S10
F15267.S11
F15267.S12
F15267.S13
F15267.S14
F15267.S15
F15267.S16
F15267.S17
F15267.S18
F15267.S19
F15267.S20
F15267.S21
F15267.S22
F15267.S23
F15267.S24
F15267.S25
F15267.S26
F15267.S27
F15267.S28
F15267.S29
F15267.S30
F15267.S31
F15267.S32
F15267.S33
F15267.S34
F15267.S35
F15267.S36
F15267.S37
F15267.S38
F15267.S39
F15267.S40
F15267.S41
F15267.S42
F15267.S43
F15267.S44
F15267.S45
F15267.S46
F15267.S47
F15267.S48
Row Sum
Percentage
input
351,069
316,882
324,194
343,908
301,523
321,622
339,917
1,743
301,412
485,186
390,053
339,171
373,430
421,668
339,984
388,320
380,529
296,233
501,909
266,758
387,884
313,861
346,875
115,954
287,342
311,676
318,224
291,804
349,528
316,869
341,266
305,230
384,565
368,774
321,348
313,307
248,203
347,109
303,428
313,820
354,569
289,749
339,047
287,264
332,418
372,400
368,506
339,802
15,756,333
100.00%
filtered
319,008
287,225
294,333
311,897
273,302
292,104
309,327
1,562
273,281
442,219
353,773
308,280
338,276
382,843
307,646
351,966
346,068
268,864
457,980
241,736
353,193
284,730
315,138
105,132
261,985
283,540
290,115
265,241
318,429
288,909
310,098
277,684
350,130
335,344
292,499
286,230
226,199
315,199
276,229
286,071
322,838
263,766
308,805
261,248
302,347
339,465
335,844
309,394
14,327,492
90.93%
denoisedF
312,422
284,333
289,424
306,009
265,408
287,280
307,052
1,541
266,442
438,667
341,671
304,014
329,079
377,583
304,359
340,896
340,939
262,371
452,123
240,796
345,764
277,977
305,522
104,431
260,844
282,477
288,695
259,088
307,580
287,380
308,914
274,711
349,223
333,647
291,449
285,327
224,984
312,603
275,097
280,086
321,024
262,848
307,645
258,923
299,771
338,479
334,079
307,035
14,138,012
89.73%
denoisedR
312,590
281,951
289,075
306,265
268,009
286,227
304,450
1,522
268,021
435,584
345,553
301,606
331,840
375,083
301,743
346,099
340,521
263,412
450,670
238,456
344,719
277,965
309,139
103,345
258,475
279,493
286,065
261,633
313,740
285,085
305,416
274,452
345,968
330,482
288,534
282,466
223,171
310,891
272,584
282,377
318,594
259,879
304,527
257,907
298,312
335,031
331,294
305,085
14,095,306
89.46%
merged
301,437
274,927
279,461
294,838
255,237
275,215
298,158
0
256,777
426,143
321,720
289,838
318,679
365,055
293,003
330,205
331,714
251,826
437,465
229,990
329,945
264,576
293,376
65,617
251,550
275,310
281,102
249,340
294,920
280,140
301,165
268,912
341,374
323,264
284,671
279,037
219,861
289,915
266,269
270,488
313,984
256,550
299,494
253,422
293,008
329,798
324,370
299,138
13,632,284
86.52%
nonchim
243,104
198,186
240,584
231,327
181,789
238,996
278,045
0
163,895
416,168
267,839
236,449
197,743
331,251
217,850
165,483
292,638
211,555
398,504
228,159
310,090
164,250
229,496
64,947
245,838
268,598
267,349
235,457
279,028
234,786
273,197
259,526
304,141
309,319
255,354
246,967
175,505
259,606
251,417
233,487
277,283
231,204
287,808
244,865
277,243
322,165
308,961
267,660
11,825,112
75.05%
This table can be downloaded as an Excel table below:
5. DADA2 Amplicon Sequence Variants (ASVs). A total of 6833 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 20210310a
The close-reference taxonomy assignment of the ASV sequences using BLASTN is based on the algorithm published by Al-Hebshi et. al. (2015)[2].
1. Raw sequences reads in FASTA format were BLASTN-searched against a combined set of 16S rRNA reference sequences - the FOMC 16S rRNA Reference Sequences version 20221029 (https://microbiome.forsyth.org/ftp/refseq/).
This set consists of the HOMD (version 15.22 http://www.homd.org/index.php?name=seqDownload&file&type=R ), Mouse Oral Microbiome Database (MOMD version 5.1 https://momd.org/ftp/16S_rRNA_refseq/MOMD_16S_rRNA_RefSeq/V5.1/),
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 full-length 16S rRNA sequences from HOMD V15.22, 356 from MOMD V5.1, and 22,126 from NCBI, a total of 23,497 sequences.
Altogether these sequence represent a total of 17,035 oral and non-oral microbial species.
The NCBI BLASTN version 2.7.1+ (Zhang et al, 2000) [3] 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)[4].
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:
Al-Hebshi NN, Nasher AT, Idris AM, Chen T. Robust species taxonomy assignment algorithm for 16S rRNA NGS reads: application
to oral carcinoma samples. J Oral Microbiol. 2015 Sep 29;7:28934. doi: 10.3402/jom.v7.28934. PMID: 26426306; PMCID: PMC4590409.
Zhang Z, Schwartz S, Wagner L, Miller W. A greedy algorithm for aligning DNA sequences. J Comput Biol. 2000 Feb-Apr;7(1-2):203-14. doi: 10.1089/10665270050081478. PMID: 10890397.
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%(>=1434 reads)
A
Total reads
22,876,785
22,876,785
B
Total assigned reads
14,343,699
14,343,699
C
Assigned reads in species with read count < MPC
0
150,651
D
Assigned reads in samples with read count < 500
901
1,587
E
Total samples
193
193
F
Samples with reads >= 500
190
188
G
Samples with reads < 500
3
5
H
Total assigned reads used for analysis (B-C-D)
14,342,798
14,191,461
I
Reads assigned to single species
12,334,639
12,250,799
J
Reads assigned to multiple species
1,436,797
1,429,857
K
Reads assigned to novel species
571,362
510,805
L
Total number of species
837
185
M
Number of single species
381
130
N
Number of multi-species
37
9
O
Number of novel species
419
46
P
Total unassigned reads
8,533,086
8,533,086
Q
Chimeric reads
195,973
195,973
R
Reads without BLASTN hits
5,381,707
5,381,707
S
Others: short, low quality, singletons, etc.
2,955,406
2,955,406
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[5][6] 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 [7].
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) at the species level.
Printed on each graph is the statistical significance p values of the difference between the groups.
The significance is calculated using either Kruskal-Wallis test or the Wilcoxon rank sum test, both are non-parametric methods (since
microbiome read count data are considered non-normally distributed) for testing
whether samples originate from the same distribution (i.e., no difference between groups). The Kruskal-Wallis test is used to compare three or more
independent groups to determine if there are statistically significant differences between their medians. The Wilcoxon Rank Sum test, also known as
the Mann-Whitney U test, is used to compare two independent groups to determine if there is a significant difference between their distributions.
The p-value is shown on the top of each graph. A p-value < 0.05 is considered statistically significant between/among the test groups.
Alpha Diversity Box Plots for All Groups - Species Level
Alpha Diversity Box Plots for Individual Comparisons at Species level
Beta diversity compares the similarity (or dissimilarity) of microbial profiles between different
groups of samples. There are many different similarity/dissimilarity metrics [8].
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, at the Species level:
NMDS and PCoA Plots for All Groups - Species Level
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 at the Species level:
NMDS and PCoA Plots for Individual Comparisons at Species level
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 [9].
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 [10]. 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.
Starting with version V1.2, we include the results of ANCOM-BC (Analysis of Compositions of
Microbiomes with Bias Correction) (Lin and Peddada 2020) [11]. 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 [12]; Grandhi, Guo, and Peddada 2016 [13]). 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) [14].
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. We provide the network association result with SparCC (Sparse Correlations for Compositional data)(Friedman & Alm 2012), which
is a method for inferring correlations from compositional data. SparCC estimates the linear Pearson correlations between
the log-transformed components.
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.
