The 16S rRNA gene amplicon sequence data from tailing and nontailing rhizosphere soils of Mimosa pudica from a heavy metal-contaminated area are reported here. Diverse bacterial taxa were represented in the results, and the most dominant phyla were Proteobacteria (41.2%), Acidobacteria (17.1%), and Actinobacteria (14.4%).
ABSTRACT
The 16S rRNA gene amplicon sequence data from tailing and nontailing rhizosphere soils of Mimosa pudica from a heavy metal-contaminated area are reported here. Diverse bacterial taxa were represented in the results, and the most dominant phyla were Proteobacteria (41.2%), Acidobacteria (17.1%), and Actinobacteria (14.4%).
ANNOUNCEMENT
The rhizosphere of plants is normally colonized by microbial communities which potentially benefit the host plants (1–3). Knowledge of the bacterial community of the metal-tolerant and leguminous Mimosa pudica (found abundantly in the studied heavy metal-contaminated soil) would explain their involvement in enhancing the growth and survival of the plant (4). Studies on microbial communities from different environments provide novel insights into their structure and function, leading to the discovery of novel functional genes (5, 6). The 16S rRNA gene amplicon sequence data presented here provide insight toward understanding how the bacterial diversity impacts plant growth promotion and heavy metal tolerance.
The rhizosphere soils of M. pudica were collected from six different sites (tailing sites, MRS1, MRS2, and MRS3; nontailing sites, MRS4, MRS5, and MRS6) of an ex-tin mining area (latitude 5°38′N, longitude 101°1′E) in Perak, Malaysia. Physicochemical analysis (7) indicated the soils to have acidic pH (4.90 to 5.75) and to be sandy loam in nature and salt free (electrical conductivity [EC] range, 0.12 to 0.79 mS/cm). Heavy metal analysis by inductively coupled plasma optical emission spectrometry (8) detected arsenic (14.3 to 1,242 mg/kg), cadmium (1.6 to 17.8 mg/kg), and lead (52.17 to 81.10 mg/kg). M. pudica roots were shaken gently to remove rhizosphere soil adhering to the surface of the roots. This was done in a laminar flow cabinet, and sterile forceps were used to remove soil tightly attached to the roots (9, 10). DNA was extracted from the rhizosphere soils using a NucleoSpin soil DNA extraction kit (Macherey-Nagel, Germany) according to the manufacturer’s instructions. PCR amplification of the V3/V4 hypervariable regions was performed using the recommended Illumina 16S rRNA gene amplicon library method (USA) (11) with the primers Bakt_341F (CCTACGGGNGGCWGCAG) and Bakt_805R (GACTACHVGGGTATCTAATCC) (12). The libraries were sequenced using the MiSeq platform (Illumina).
Adapter sequences and low-quality reads were removed from the paired-end reads using BBDuk from the BBTools package (https://sourceforge.net/projects/bbmap/) (13), and forward and reverse reads were merged using USEARCH v11.0.667 (14, 15). Default parameters were used for all software unless otherwise specified. All sequences shorter than 150 bp or longer than 600 bp were removed from downstream processing. The reads were aligned with the SILVA 16S rRNA gene database (release 132) (16), inspected for chimeric errors using VSEARCH v2.6.2 (17), and then clustered de novo into operational taxonomic units (OTUs) at 97% similarity using UPARSE v11.0.667 (18). The taxonomic assignment of the OTUs was achieved using QIIME v1.9.1 (19–21) against the SILVA database (16). All statistical analyses were done in the R statistical package v3.6.1 (https://www.r-project.org/) (22).
The total number of reads obtained in this study was 125,158 (Table 1). The OTUs were assigned to 23 bacterial phyla, 72 classes, 165 orders, 248 families, and 357 genera. Proteobacteria (41.2%), Acidobacteria (17.1%), and Actinobacteria (14.4%) were the most represented phyla, and the relative abundance of the top bacterial phyla in each sample is shown in Fig. 1.
TABLE 1.
Summary description of sample data in this study
| Site | Sample | SRA accession no. | No. of sequences | No. of OTUs | Amplicon read length (bp) |
|---|---|---|---|---|---|
| Tailing | MRS1 | SRR10909566 | 9,995 | 957 | 608 |
| MRS2 | SRR10909565 | 26,105 | 1,306 | 607 | |
| MRS3 | SRR10909564 | 9,199 | 942 | 603 | |
| Nontailing | MRS4 | SRR10909563 | 28,389 | 1,213 | 604 |
| MRS5 | SRR10909562 | 27,898 | 1,308 | 599 | |
| MRS6 | SRR10909561 | 23,572 | 1,285 | 568 |
FIG 1.
Relative abundance of the top bacterial phyla in each sample obtained from the sequencing data. Each color represents a different phylum.
Data availability.
The 16S rRNA gene amplicon sequencing data from this study were deposited in the Sequence Read Archive (SRA) of the National Center for Biotechnology Information (NCBI) under the BioProject accession number PRJNA601794 (Table 1).
ACKNOWLEDGMENTS
This work was supported by a Ministry of Higher Education, Malaysia (MOHE), grant (number 203/PBIOLOGI/6711774) and a Universiti Sains Malaysia Bridging Grant (grant number 304/PBIOLOGI/6316511). The funders had no role in study design, data collection and interpretation, or the decision to submit the work for publication.
We also thank Mardani Abdul Halim of the School of Biological Sciences, Universiti Sains Malaysia, for constructive comments and suggestions.
All authors have read and approved the manuscript and declare no conflicts of interest in the submission.
REFERENCES
- 1.Lopez S, Goux X, Echevarria G, Calusinska M, Morel JL, Benizri E. 2019. Community diversity and potential functions of rhizosphere-associated bacteria of nickel hyperaccumulators found in Albania. Sci Total Environ 654:237–249. doi: 10.1016/j.scitotenv.2018.11.056. [DOI] [PubMed] [Google Scholar]
- 2.Ju W, Liu L, Fang L, Cui Y, Duan C, Wu H. 2019. Impact of co-inoculation with plant-growth-promoting rhizobacteria and rhizobium on the biochemical responses of alfalfa-soil system in copper contaminated soil. Ecotoxicol Environ Saf 167:218–226. doi: 10.1016/j.ecoenv.2018.10.016. [DOI] [PubMed] [Google Scholar]
- 3.Khanna K, Jamwal VL, Gandhi SG, Ohri P, Bhardwaj R. 2019. Metal resistant PGPR lowered Cd uptake and expression of metal transporter genes with improved growth and photosynthetic pigments in Lycopersicon esculentum under metal toxicity. Sci Rep 9:5855. doi: 10.1038/s41598-019-41899-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 4.Xavier JC, Costa PES, Hissa DC, Melo VMM, Falcão RM, Balbino VQ, Mendonça LAR, Lima MGS, Coutinho HDM, Verde LCL. 2019. Evaluation of the microbial diversity and heavy metal resistance genes of a microbial community on contaminated environment. Appl Geochem 105:1–6. doi: 10.1016/j.apgeochem.2019.04.012. [DOI] [Google Scholar]
- 5.Klonowska A, Moulin L, Ardley JK, Braun F, Gollagher MM, Zandberg JD, Marinova DV, Huntemann M, Reddy TBK, Varghese NJ, Woyke T, Ivanova N, Seshadri R, Kyrpides N, Reeve WG. 2020. Novel heavy metal resistance gene clusters are present in the genome of Cupriavidus neocaledonicus STM 6070, a new species of Mimosa pudica microsymbiont isolated from heavy-metal-rich mining site soil. BMC Genomics 21:214. doi: 10.1186/s12864-020-6623-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 6.Gu Y, Van Nostrand JD, Wu L, He Z, Qin Y, Zhao F-J, Zhou J. 2017. Bacterial community and arsenic functional genes diversity in arsenic contaminated soils from different geographic locations. PLoS One 12:e0176696. doi: 10.1371/journal.pone.0176696. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Motsara MR, Roy RN. 2008. Guide to laboratory establishment for plant nutrient analysis. FAO Fertilizer Plant Nutr Bull 19. [Google Scholar]
- 8.Bettinelli M, Beone GM, Spezia S, Baffi C. 2000. Determination of heavy metals in soils and sediments by microwave-assisted digestion and inductively coupled plasma optical emission spectrometry analysis. Anal Chim Acta 424:289–296. doi: 10.1016/S0003-2670(00)01123-5. [DOI] [Google Scholar]
- 9.McPherson MR, Wang P, Marsh EL, Mitchell RB, Schachtman DP. 2018. Isolation and analysis of microbial communities in soil, rhizosphere, and roots in perennial grass experiments. J Vis Exp 2018:57932. doi: 10.3791/57932. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Qiao Q, Wang F, Zhang J, Chen Y, Zhang C, Liu G, Zhang H, Ma C, Zhang J. 2017. The variation in the rhizosphere microbiome of cotton with soil type, genotype and developmental stage. Sci Rep 7:3940. doi: 10.1038/s41598-017-04213-7. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Illumina. 2013. 16S metagenomic sequencing library preparation: preparing 16S ribosomal RNA gene amplicons for the Illumina MiSeq system. Illumina, San Diego, CA. [Google Scholar]
- 12.Herlemann DPR, Labrenz M, Jurgens K, Bertilsson S, Waniek JJ, Andersson AF. 2011. Transitions in bacterial communities along the 2000 km salinity gradient of the Baltic Sea. ISME J 5:1571–1579. doi: 10.1038/ismej.2011.41. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13.Bushnell B, Rood J, Singer E. 2017. BBMerge—accurate paired shotgun read merging via overlap. PLoS One 12:e0185056. doi: 10.1371/journal.pone.0185056. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Edgar RC. 2010. Search and clustering orders of magnitude faster than BLAST. Bioinformatics 26:2460–2461. doi: 10.1093/bioinformatics/btq461. [DOI] [PubMed] [Google Scholar]
- 15.Liu T, Chen C-Y, Chen-Deng A, Chen Y-L, Wang J-Y, Hou Y-I, Lin M-C. 2020. Joining Illumina paired-end reads for classifying phylogenetic marker sequences. BMC Bioinformatics 21:105. doi: 10.1186/s12859-020-3445-6. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 16.Glöckner FO. 2019. The SILVA database project: an ELIXIR core data resource for high-quality ribosomal RNA sequences. Biodivers Inf Sci Stand 3:e36125. doi: 10.3897/biss.3.36125. [DOI] [Google Scholar]
- 17.Rognes T, Flouri T, Nichols B, Quince C, Mahé F. 2016. VSEARCH: a versatile open source tool for metagenomics. PeerJ 4:e2584. doi: 10.7717/peerj.2584. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Edgar RC. 2013. UPARSE: highly accurate OTU sequences from microbial amplicon reads. Nat Methods 10:996–998. doi: 10.1038/nmeth.2604. [DOI] [PubMed] [Google Scholar]
- 19.Caporaso JG, Kuczynski J, Stombaugh J, Bittinger K, Bushman FD, Costello EK, Fierer N, Peña AG, Goodrich JK, Gordon JI, Huttley GA, Kelley ST, Knights D, Koenig JE, Ley RE, Lozupone CA, McDonald D, Muegge BD, Pirrung M, Reeder J, Sevinsky JR, Turnbaugh PJ, Walters WA, Widmann J, Yatsunenko T, Zaneveld J, Knight R. 2010. QIIME allows analysis of high-throughput community sequencing data. Nat Methods 7:335–336. doi: 10.1038/nmeth.f.303. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Bolyen E, Rideout JR, Dillon MR, Bokulich NA, Abnet CC, Al-Ghalith GA, Alexander H, Alm EJ, Arumugam M, Asnicar F, Bai Y, Bisanz JE, Bittinger K, Brejnrod A, Brislawn CJ, Brown CT, Callahan BJ, Caraballo-Rodríguez AM, Chase J, Cope EK, Da Silva R, Diener C, Dorrestein PC, Douglas GM, Durall DM, Duvallet C, Edwardson CF, Ernst M, Estaki M, Fouquier J, Gauglitz JM, Gibbons SM, Gibson DL, Gonzalez A, Gorlick K, Guo J, Hillmann B, Holmes S, Holste H, Huttenhower C, Huttley GA, Janssen S, Jarmusch AK, Jiang L, Kaehler BD, Kang KB, Keefe CR, Keim P, Kelley ST, Knights D, et al. 2019. Reproducible, interactive, scalable and extensible microbiome data science using QIIME 2. Nat Biotechnol 37:852–857. doi: 10.1038/s41587-019-0209-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 21.Wu H, Irizarry RA, Bravo HC. 2010. Intensity normalization improves color calling in SOLiD sequencing. Nat Methods 7:336–337. doi: 10.1038/nmeth0510-336. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.R Core Team. 2020. R: a language and environment for statistical computing. R Foundation for Statistical Computing, Vienna, Austria. [Google Scholar]
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Data Availability Statement
The 16S rRNA gene amplicon sequencing data from this study were deposited in the Sequence Read Archive (SRA) of the National Center for Biotechnology Information (NCBI) under the BioProject accession number PRJNA601794 (Table 1).

