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The Role of Vertical Transmission of Shoot Endophytes in Root-Associated Microbiome Assembly and Heavy Metal Hyperaccumulation in Sedum alfredii Jipeng Luo, Qi Tao, Radek Jupa, Yuankun Liu, Keren Wu, Yuchao Song, Jinxing Li, Yue Huang, Linyun Zou, Yongchao Liang, and Tingqiang Li Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.9b01093 • Publication Date (Web): 30 May 2019 Downloaded from http://pubs.acs.org on June 4, 2019
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TITLE
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The Role of Vertical Transmission of Shoot Endophytes in Root-Associated
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Microbiome Assembly and Heavy Metal Hyperaccumulation in Sedum alfredii
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Corresponding author: Tingqiang Li, Ph.D. and Professor, College of Environmental and
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Resource Sciences, Zhejiang University, Hangzhou 310058, China; Tel: +86-571-88982518,
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Fax: +86-571-88982907, E-mail:
[email protected] 8
Jipeng Luo,*† Qi Tao,*‡ Radek Jupa,§Yuankun Liu,† Keren Wu,† Yuchao Song,†
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Jinxing Li,† Yue Huang,† Linyun Zou,† Yongchao Liang,† Tingqiang Li†
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† Ministry of Education Key Laboratory of Environmental Remediation and Ecological
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Health, College of Environmental and Resource Sciences, Zhejiang University, Hangzhou
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310058, China.
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‡College of Resources, Sichuan Agricultural University, Chengdu 611130, China
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§Department of Experimental Biology, Faculty of Science, Masaryk University, Kotlářská
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2, 61137 Brno, Czech Republic.
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*These authors contributed equally to this work
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Author contributions: J.L., Q.T. and T.L. designed the experiments; J.L., Q.T., Y.L., Y.H.,
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L.Z., K.W., J.L. and Y.S. performed the experiments; J.L. and Q.T. analyzed the data; J.L.,
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Q.T., R.J.,Y.L., and T.L. wrote the manuscript with contribution of all of the coauthors; T.L.
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supervised the experiments and writing of the article.
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Conflict of interest: The authors declare that they have no competing interests.
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ABSTRACT: The transmission mode of shoot-associated endophytes in hyperaccumulators
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and their roles in root microbiome assembly and heavy metal accumulation remains unclear.
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Using 16S rRNA gene profiling, we investigated the vertical transmission of
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shoot-associated endophytes in relation to growth and Cd/Zn accumulation of Sedum alfredii
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(Crassulaceae). Endophytes were transmitted from shoot cuttings to the rhizocompartment
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of new plants in both sterilized (γ-irradiated) and native soils. Vertical transmission was far
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more efficient in the sterile soil and the transmitted endophytes have become a dominant
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component of the newly established root-associated microbiome. Based on 16S rRNA genes,
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the vertically-transmitted taxa were identified as the families of Streptomycetaceae,
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Nocardioidaceae, Pseudonocardiaceae, and Rhizobiaceae. Abundances of Streptomycetaceae,
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Nocardioidaceae and Pseudonocardiaceae were strongly correlated with increased shoot
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biomass and total Cd/Zn accumulation. Inoculation of S. alfredii with the synthetic bacterial
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community sharing the same phylogenetic relatedness with the vertically transmitted
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endophytes resulted in significant improvements in plant biomass, root morphology, and
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Cd/Zn accumulation. Our results demonstrate that successful vertical transmission of
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endophytes from shoots of S. alfredii to its rhizocompartment is possible, particularly in soils
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with attenuated microbiomes. Furthermore, the endophyte-derived microbiome plays an
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important role in metal hyperaccumulation.
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Table of Contents Graphic
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1. INTRODUCTION
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Land plants harbor a diverse array of bacterial microbiota on and inside their tissues.
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These microbiota affect plant growth and health, and therefore success in a large variety of
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ways.1,2 It is well known that plants rely on their endophytic microbiota for nutrient
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acquisition,3 growth promotion,4 suppression of phytopathogens and stress tolerance.5,6
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However, the wider role of the microorganisms, particularly the role of the shoot-associated
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(leaf and stem) microbiota rather than the well-studied root-associated bacterial assemblages,
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on plant success is still being unraveled.7-9 Furthermore, endophytic bacteria are likely to be
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highly important symbionts affecting the host plants interaction with the abiotic and biotic
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environments. These endosymbionts establish an intimate symbiosis within plant tissues and
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their survival and reproduction depends largely on the plant.10 In this case, the success of the
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endophyte is coupled with the success of the host.
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The transmission mode is an important feature of endophytes. Generally, the endophytic
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microbiome may be assembled either through horizontal transmission from the environment
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to host and/or via vertical transmission from parent to progeny.9,11 It is commonly
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considered that root endophytes are predominantly assembled via horizontal transmission
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(recruitment of microorganisms from the surrounding soil).7-9 However, numerous studies
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have recently confirmed the existence of vertical (seed-based) transmission of endophytes in
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plant species such as rice,12 Brassicaceae13 and some representatives of grasses.14 These
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studies highlighted that seed endophytes could migrate to the newly established root
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endosphere or rhizosphere compartment. However the mechanisms and factors affecting the
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vertical transmission of endophytes remain elusive for most host-endophyte associations. In
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addition, vertical transmission of endosymbionts has not been described in hyperaccumulator
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species.
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Endophytic bacteria can alter the interactions of plants with metals in the environment,
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and this trait can be used to maximize the potential for phytoremediation of metal
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contaminated sites.15 However, the maintenance of the appropriate endophytic taxa by the
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host plant and their inheritance to following plant generations are important prerequisites for
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the long-term success
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Cd-hyperaccumulator Sedum alfredii (Crassulaceae) found that root microbiomes were
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primarily derived from the taxa resident in the soil surrounding roots rather than vertically
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transmitted as seed-borne endophytes.16 This implies that endophytes present in the seed of S.
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alfredii may not be successful competitors against soil microorganisms, resulting in failure
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in their transmission to the new generation of plants. Nevertheless, shoot cuttings, separated
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from hyperaccumulators grown on metal contaminated sites, were shown to carry large
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amounts of endophytes with great potential to survive in metal-stress conditions.17 The
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recruitment of these endophytes altered plant growth characteristics and heavy metal
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hyperaccumulation.18 Therefore, vertical transfer of endophytes (and the traits they confer)
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via shoot cuttings is likely possible for some hyperaccumulator species. However, direct
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evidence supporting this hypothesis is unavailable yet. Moreover, a handful of experimental
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studies have illustrated that the vertically-transmitted seed endophytes of rice and bean could
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propagate as part of the new plant microbiota,12,19 indicating that the seed-borne
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endosymbionts were involved in root-associated microbiome assembly. However, whether
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shoot endophytes of hyperaccumulators will become important founders of the newly
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established root microbiomes via vertical transmission, remains unknown.
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of
this
function.
For
example,
experiments
using
the
Under metal stress, endophytic bacteria can promote plant growth by producing
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phytohormones,
increasing
nutrient
solubility
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1-aminocyclopropane-1-carboxylate (ACC) deaminase,1,15 as well as alleviate the damages
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of heavy metals to plants by altering the bioavailability/or toxicity of heavy metal.15,18 Given
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the extent of plant-endophyte associations and physiological processes involved, it is not
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surprising that considerable number of researches have been conducted with goal of utilizing
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endophytic bacteria to optimize phytoremediation systems and enhance their use.20,21
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However, most empirical studies on the functions of endophytes have implemented
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inoculation–based transfer of the microbiome within artificial cultivation (laboratory)
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systems; these do not generally consider mechanisms of vertical transmission.
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S. alfredii is well known as an important Zn/Cd co-hyperaccumulator that can be easily
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propagated using shoot cuttings.22,23 In this species, cultivation of shoot cuttings has been
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used to investigate mechanisms of Cd/Zn uptake, xylem transport, and Cd/Zn tolerance.24,25
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Studies indicated that S. alfredii are host to a diversity of metal-tolerant endophytes that
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could promote plant growth and heavy metal accumulation.16,21 However, the
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community-level dynamics of shoot endophytic microbiome composition and their effects on
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root microbiome acquisition and assembly in natural conditions remains unknown. In this
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study, using S. alfredii as a model plant, we investigated the transmission of endophytic
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bacteria from shoot cuttings to root-associated compartments, and examined the effects of
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the newly established microbiomes on plant growth and metal accumulation.
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2. MATERIALS AND METHODS
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2.1. Plant and Soil Collection. Mature plants of S. alfredii were collected in an old
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Pb/Zn mining area in Quzhou city, Zhejiang province, China. Simultaneously with plants,
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top soil (10 cm) were collected, and then were air dried, sieved (< 2 mm) and separated into
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two parts. One part was exposed to gamma ray irradiation (30 kGy; γ-irradiated soil), while
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the other part was untreated (native soil). Basic physicochemical properties of this soil
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(Table S1) were determined according to the previously described standard procedures.16
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For plant cultivation, shoot cuttings with similar size and comparable leaf numbers were
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separated from mother plants. The newly exposed (cut) surfaces of the offshoot clones were
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sterilized in 70% (v/v) ethanol for 30s, 3% (w/v) sodium hypochlorite solution for 150s, and
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then washed six times with sterile water.
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2.2. Experimental Design, Plant and Microbiota Cultivation. The γ-irradiated and
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native soils were used to investigate the vertical transmission of shoot endophytes by shoot
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cuttings propagation. Subsequently, the hydroponic and tissue culture experiments were
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conducted, by inoculating S. alfredii with the candidate vertically-transmitted bacterial
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isolates (Table S2), to assess the effects of these bacteria on plant growth, root development
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and heavy metals accumulation. For each of these three cultivation experiments, plants were
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grown under standard growth-chamber conditions: 16-h photoperiod, 300 μmol m−2s−1 of
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average light intensity, 26/20°C of day/night temperature, 75% of relative humidity.
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For soil cultivation, shoot cuttings of S. alfredii were surface-sterilized and then
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transplanted into the ‘rhizosphere compartment’ of a rhizobox filled with either 2.5 kg of
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γ-irradiated or native soil.26 The ‘non-rhizosphere chamber’ of rhizobox (without plants) was
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treated as bulk soil. Pots without plants were defined as unplanted treatment. Each treatment
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had five replicates. The soil was moistened with sterile water and gravimetrically adjusted
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every 4 days to 60% of water holding capacity. After four months of cultivation, shoot
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biomass and accumulation of heavy metal were determined as described in the
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Supplementary Information. The collection of bulk soil, rhizosphere soil, and root
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endosphere samples was performed as described in a previous study.16 The collected samples
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were immediately frozen in liquid nitrogen and stored at -80℃ until subsequent analysis.
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For hydroponic cultivation, S. alfredii shoot cuttings were surface-sterilized and
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cultured in axenic nutrient solution24 either with or without 25μM Cd(NO3)2 and 500μM
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ZnSO4. The nutrient solutions were inoculated with a synthetic microbial community
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consisting of four endophytic bacterial isolates (strains SaSS1, SaSS28, SaSS40, and SaSS46;
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Table S2) originating from the shoot of S. alfredii plants. These strains share a similar
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phylogenetic relatedness with the potential vertically-transmitted endophytes and show high 7
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resistance to Cd and Zn (details of the acquisition of bacterial inocula are provided in
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Supplementary Information). Treatments included Control (pure axenic nutrient solution),
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Cd2+ and Zn2+ treatment (HM), and a combination of HM and bacterial strains (HM+Bact).
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Each treatment was replicated four times, and plants were harvested after 60 days.
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Tissue-based cultivation was performed to investigate the effects of the four
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aforementioned bacterial strains on root morphology and plant development. Briefly, stem
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offshoots were cut transversely into 0.5 cm segments and transferred to MS medium
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solidified with 0.7% agar. The experiment comprised four treatments: (i) Pure MS medium
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(Control); (ii) MS medium containing 5μM Cd(NO3)2 and 50μM ZnSO4 (HM); (iii) MS
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medium contains four bacterial strains (1×107of total bacterial cell numbers g-1 agar) (Bact);
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and (iv) MS medium containing 5μM Cd(NO3)2 and 50μM ZnSO4 and four bacterial strains
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(HM+Bact). Root length and plant biomass were measured after two months of cultivation.
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2.3. DNA Extraction, Quantitative Real-Time PCR (qPCR), and Amplification
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Sequencing. The stem and leaf samples at the time of transplantation, and root samples
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after four months of soil cultivation were mechanically homogenized. DNA was extracted
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from the homogenized tissues, along with unplanted, bulk, and rhizosphere soils. Similarly,
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RNA was extracted from the root samples from the hydroponic experiment using a
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commercially available kit. The total bacterial cell numbers and relative expression of root
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transporter genes (Table S3) were determined by qPCR. Extraction procedures and the
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protocol of qPCR are described in detail in the Supplementary information.
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In order to capture the true diversity of bacterial communities in the shoot- and
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root-associated compartment samples, the V5-V7 and V3-V4 regions of the 16S rRNA gene
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were amplified, respectively. 27 The DNA extracted from soil and root samples was used as
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template for amplification of the 16S rRNA gene V3-V4 region with the primer set
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S-D-Bact-0341-b-S-17 and S-D-Bact-0785-a-A-21.28 For the leaf and stem DNA samples,
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the 16S rRNA gene V5-V7 region was amplified with the primer set 799f and 1193r,29,30
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selected as it shows very low amplification of non-target DNA (e.g. chloroplast and
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mitochondria) and retrieves a high number of bacterial reads.27. Each sample was amplified
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with a primer set link a dual-index barcode. This enabled sequencing of pooled (equimolar)
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amplicons (MiSeq; Illumina) and downstream assignment of amplicons to treatments based
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on the unique barcodes. Sequence data were submitted to the NCBI Sequence Read Archive
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under Bioproject PRJNA432836 and BioSample accession numbers from SAMN08462835
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to SAMN08462884.
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2.4. Sequence-Data Processing and Analyses. A total of 1,639,312 sequences was
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obtained after quality control, with a median read count per sample of 29,284 (range:
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22,368-83,117). The bioinformatic analyses of raw sequence data including de-multiplex,
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quality control, and taxonomy classification were performed using the QIIME2 (v.2018.8)
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software.31 The DADA232 method was used to perform sequence quality control, in which
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the reads were denoised into amplicon sequence variants (ASVs), and then a feature table
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was generated. Taxonomic classification of the denoised sequences was performed by
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training the naive Bayse classifier using Silva 132 99% OTUs (Operational Taxonomic
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Units) full-length reference sequences. Additionally, the ASV table was normalized by
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rarefying to 8000 reads per sample to reduce the bias of different sequencing depth between
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samples. For detailed description of sequence processing, see the Supplementary
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Information.
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2.5. Fluorescence in Situ Hybridization (FISH). We applied FISH to visualize bacteria
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and Actinobacteria within S. alfredii stem, root and rhizopshere soil samples according to a
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previously described protocol.33
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2.6. Statistical Analyses. The statistical analyses were mainly performed in R software
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(http://www.r-project.org) using the sequence data set of 5331 ASVs across 50 samples, and
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the detailed descriptions of individual analyses are provided in the Supplementary
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Information.
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3. RESULTS
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3.1. Plant Growth and Heavy Metal Accumulation. S. alfredii growth was
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significantly promoted when cultivated in γ-irradiated soil (Figure 1a, b). The fresh weight
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(FW) and dry weight (DW) of plant shoots cultivated in γ-irradiated soil were significantly
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increased by 104% (P=0.005) and 122% (P=0.015) compared with plants grown in the
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native soil (Figure1c). The concentrations of Cd and Zn in shoots were also higher in plants
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grown in the γ-irradiated soil than in the native soil (Figure 1d). Specifically, S. alfredii
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extracted 1389.1 mg Cd and 25064.2 mg Zn kg-1 dry shoot biomass from the γ-irradiated soil
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at the harvest, which were 4.6-fold and 4.3-fold higher than that from the native soil,
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respectively.
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In hydroponic experiment, bacterial inoculation significantly (P