Subscriber access provided by The University of Texas at El Paso (UTEP)
Remediation and Control Technologies
Bacterial survival strategies in an alkaline tailing site and the physiological mechanisms of dominant phylotypes as revealed by metagenomic analyses Weimin Sun, Enzong Xiao, Max Häggblom, Valdis Krumins, Yiran Dong, Xiaoxu Sun, Fangbai Li, Qi Wang, Baoqin Li, and Bei Yan Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.8b03853 • Publication Date (Web): 22 Oct 2018 Downloaded from http://pubs.acs.org on October 23, 2018
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 33
Environmental Science & Technology
1
Bacterial survival strategies in an alkaline tailing site and the physiological mechanisms of
2
dominant phylotypes as revealed by metagenomic analyses
3
Weimin Sun1*†, Enzong Xiao2†, Max Häggblom3, Valdis Krumins4, Yiran Dong5, Xiaoxu Sun1, Fangbai Li1, Qi
4
Wang1, Baoqin Li1, Bei Yan1
5
1. Guangdong Key Laboratory of Integrated Agro-environmental Pollution Control and Management,
6
Guangdong Institute of Eco-environmental Science & Technology, Guangzhou 510650, China
7 8 9
2. Key Laboratory of Water Quality and Conservation in the Pearl River Delta, Ministry of Education, School of Environmental Science and Engineering, Guangzhou University, Guangzhou 510006, China 3. Department of Biochemistry and Microbiology, Rutgers University, New Brunswick NJ 08901, USA
10
4. Department of Environmental Sciences, Rutgers University, New Brunswick, NJ 08901, USA
11
5. Institute for Genomic Biology, University of Illinois, Urbana-Champaign, Urbana IL 61801, USA
12 13
*Correspondence to:
14
Dr. Weimin Sun
15
808 Tianyuan Road, Guangzhou, Guangdong, China. Phone: 86-020- 87024633. Fax: 86-020-87024123. E-mail:
16
[email protected] 17
†These authors contributed equally to this work.
18 19 20 21 22 1
ACS Paragon Plus Environment
Environmental Science & Technology
Page 2 of 33
23 24
Abstract
25
Microorganisms inhabiting mine tailings require specific metabolic strategies to survive, which may hold the
26
potential to clean up the pollution. Effective in situ bioremediation will rely on an in-depth understanding of the
27
function of the bacterial communities, especially the abundant and metabolically active phylotypes. In this study,
28
the bacterial communities collected from an alkaline tailing site were profiled by 16S rRNA gene amplicon
29
sequencing as well as shotgun metagenomic analysis. Our results indicated that potential for carbon and nitrogen
30
fixation as well as metal resistance and transformation were widespread among the bacterial community members,
31
especially in highly enriched phylotypes, such as members of Thiobacillus and Meiothermus. Important functional
32
microbial guilds including carbon and nitrogen fixers may contribute to phytoremediation by providing nutrients
33
for hyperaccumulator plants. In addition, metal-metabolizing bacteria may influence metal speciation and
34
solubility. This discovery provides an understanding for microbial survival strategies in the tailings and lays the
35
foundation for future potential manipulation of the tailing microbiome for in situ bioremediation.
36 37
Key words: Metal-microbe interactions; Random Forest; Shotgun metagenomics; Binning; Meiothermus
38
2
ACS Paragon Plus Environment
Page 3 of 33
Environmental Science & Technology
39
Introduction
40
Mine tailings generated by disposal of mining waste usually result in adverse metal-rich environments for
41
microbial growth
42
microbial functions 5-7. In addition to metal(loid) toxicity, mine tailings are typically nutrient-poor, making them
43
relatively inhospitable for both plants and microorganisms 8. Despite the high toxicity and low nutrient availability,
44
several studies have reported that diverse microbial communities were present in these ecosystems and played
45
important ecological roles in tailing environments 9-11. For example, microorganisms develop a range of survival
46
strategies to mitigate the toxic damage caused by metal(loid)s. Some of these strategies can influence the transport
47
and fate of metal(loid)s by affecting their speciation and solubility and thus may either increase or decrease the
48
toxicity of metal(loid)s in the environment
49
determine the rate of release of metals and sulfur to the environment 15. Numerous bacteria and archaea isolated
50
from mining area have been shown to have important roles in generating mine drainage
51
cycling of Fe and S
52
contributed to nutrient accumulation in these extreme environments 18, 19. Additionally, recent “omics” techniques
53
indicated that carbon and nitrogen fixation and sulfur oxidation was adapted by microorganisms inhabiting
54
lead/zinc mine tailings
55
primarily autotrophic metabolism as well as metal resistance 21, providing additional evidence of unique microbial
56
survival strategies in mine tailing environments.
1, 2.
Exposure to these can decrease microbial diversity and biomass
17.
12-14.
3, 4
and impair specific
Several studies indicate that microorganisms may ultimately
16
and impacting the
Isolation and detection of nitrogen fixing bacteria from tailings suggested that they
20.
In another study, the microbiome of an acid mine drainage was shown to exhibit a
57 58
The acid mine tailings produced from oxidation of sulfide-bearing minerals are global environmental problems
59
and have been well-studied with various reviews focusing on the microbiology
60
bioremediation strategies 24. Although sharing similar characteristics with acidic mine tailings (e.g., metal-rich,
15, 22,
geochemistry
23,
and
3
ACS Paragon Plus Environment
Environmental Science & Technology
Page 4 of 33
61
nutrient-poor and rapid weathering processes), alkaline tailings have been relatively less studied. In comparison
62
to acidic mine tailings, the mineralogy of alkaline tailings generally provides more suitable geochemical
63
conditions for soil development, which subsequently enables the revegetation of the tailings and establishment of
64
more stable and sustainable habitat
65
accelerating the soil development in alkaline tailings via promoting mineral precipitation and nutrient
66
accumulation
67
tailings, however, has not been specifically addressed. Such information may provide an attractive direction for
68
directing the management of contaminated tailing sites, especially for alkaline tailings. Through the use of the
69
recent omics-related techniques, it is possible to track the metabolic potential of the indigenous microbial
70
community. In addition, the development of statistical tools, such as the ensemble model, provides a means to
71
study the environment-microbe interactions derived from high throughput sequencing data 26, 27.
25.
25.
Microbial activities are thought to play important ecological roles by
An in-depth understanding of the metabolic capabilities of the innate microbiota in alkaline
72 73
In this study, we selected an alkaline tailing site which received tailings from Sb mining fifteen years ago but has
74
since received tailings from Pb/Zn mining. The shift of tailing sources created a metal gradient along the path of
75
the tailing flow and a deficiency in nutrients in the whole tailing site. Therefore, the study site is an excellent
76
natural habitat to study the microbial survival and evolution strategies in response to these two perturbations:
77
metal(loid)s contamination and nutrient limitation in alkaline tailings. Here, geochemical analyses, 16S rRNA
78
gene sequencing, statistical analyses, and metagenomic binning were coupled to reveal the microbial survival
79
strategies. The overall goals of this study are to understand: (i) the bacterial diversity and community inhabiting
80
the alkaline tailing site and (ii) the metabolic potentials of the indigenous microbiota, with a focus on the dominant
81
phylotypes.
82 4
ACS Paragon Plus Environment
Page 5 of 33
Environmental Science & Technology
83
Materials and Methods
84
Soil sampling
85
The study site was located in a Pb-Zn and Sb tailing site in Nandan County, Guangxi, China (Figure S1). The
86
tailing site was geographically divided into three zones (Zones I, II and III). The GPS coordinates were as follows:
87
Zone I: 24.852086°N, 107.672283°E; Zone II: 24.852089°N,107.672286°E; and Zone III: 24.852086°N,
88
107.672286°E. A total of 34 tailing samples for both geochemical and molecular analyses (designated CSWK01-
89
34) were taken from the upper 20 cm of the sediments using a sterile soil sampler (Table S1). The samples were
90
cooled to 3-4 °C immediately after sampling for shipment to the laboratory, where they were then stored at -80 °C
91
until analysis. The geochemical analyses of environmental parameters such as pH, total C, total N, and metals
92
and metalloids are provided in the supplementary information.
93 94
Illumina MiSeq sequencing of 16S rRNA genes
95
Total genomic DNA was extracted from 0.5 g of tailing samples using PowerSoil® Soil DNA Isolation kit (MO
96
BIO Laboratories, Inc. Carlsbad, CA) according to the manufacture’s protocol. Amplicon sequencing was
97
performed on an Illumina MiSeq platform at Ecogene (Shenzhen, China) of the V4-V5 hypervariable region of
98
the 16S rRNA genes 28. Details regarding the pipeline for 16S rRNA analysis is provided in the supplementary
99
information. Numerical analyses such as Random Forest (RF) ensemble model and co-occurrence network was
100
used to correlate the interaction among geochemical parameters and bacterial community and diversity. The
101
details to perform RF and co-occurrence network analysis were described in a previous study 26 and are briefly
102
summarized in the supplementary materials.
103 104
Metagenome sequencing and analysis 5
ACS Paragon Plus Environment
Environmental Science & Technology
Page 6 of 33
105
Metagenomic libraries from four tailing samples (one sample each from zones I and II, and two from zone III)
106
were sequenced on the Illumina Hiseq 4000 platform (paired-end 150 bp reads) at Novogene (Tianjing, China).
107
Metagenomic libraries were generated using NEB Next® Ultra™ DNA Library Prep Kit for Illumina (NEB, USA)
108
following the manufacturer’s protocols. A total of 88 Gb raw sequence data was generated (222,104,532 raw
109
reads) from four metagenomes. Raw data were first processed by Trimmomatic 0.36 for adapter removal and
110
moderate quality trimming to obtain “clean” data for subsequent data analysis as follows: raw sequence reads that
111
contained a quality score less than 38 for more than 40 bp, more than 10 bp ambiguous “N”, and/or an overlap
112
with the adapter in excess of 15 bp were discarded to obtain “clean” data for subsequent data analysis (Table S2
113
for detailed information) 29. Metagenomes were assembled using metaSPAdes from SPAdes v3.10
114
trimmed reads were mapped to the contigs using Bowtie2 version 2.2.9 31. Contigs shorter than 1kb or with an
115
average coverage less than five were discarded from the assembly. The taxonomic assignment of the sequences
116
was conducted using the Last Common Ancestor method with default parameters
117
analysis was performed by mapping sequences to KEGG,COG and/or SEED 32, 34. Raw sequences of 16S rRNA
118
and metagenomics reads have been made available in the NCBI Sequence Read Archive (SRP131706).
32, 33,
30,
and the
while the functional
119 120
Binning of metagenomics contigs
121
Contigs were binned using CONCOCT (version 0.4.0) with default settings (Table S3 for detailed information)35.
122
CheckM 1.0.6 was used to assess the completeness and contamination of the recovered genome bins 36. Genome
123
bins with completeness >80 % were classified as “high quality”, and were re-binned using the CONCOCT
124
workflow. The resulting bins were again evaluated with CheckM. Only re-binned genome bins with completeness
125
>80% were used for detailed downstream analyses. The abundance of each bin under different treatments was
126
estimated by mapping the high-quality reads of individual datasets to the contigs from bins using Bowtie 2. The
127
taxonomic and functional annotations for various genomic bins are provided in supplementary information. 6
ACS Paragon Plus Environment
Page 7 of 33
Environmental Science & Technology
128 129
Results
130
Geochemical conditions
131
A number of geochemical parameters, which can be divided into nutrients for microbial growth and metal(loid)s,
132
were measured within the tailing samples (Figure S2 and Table S4). All samples were alkaline (ranging from 7.7
133
to 10.8) except for CSWK03 (pH: 4.4). The percentage of total N (TN), total C (TC), total H (TH), total S (TS),
134
total organic carbon (TOC), and soluble S (SS) were measured as parameters essential for microbial growth.
135
Among these, TC represented 2.5±1.3 % (average ± standard deviation) of the sample weight, but TOC only
136
accounted for 0.4±0.8% of the sample weight. In most samples, TOC accounted for