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Rhizosphere microorganisms can influence the timing of plant flowering

Microbiome volumeĀ 6, ArticleĀ number:Ā 231 (2018) Cite this article

Abstract

Background

Plant phenology has crucial biological, physical, and chemical effects on the biosphere. Phenological drivers have largely been studied, but the role of plant microbiota, particularly rhizosphere microbiota, has not been considered.

Results

We discovered that rhizosphere microbial communities could modulate the timing of flowering of Arabidopsis thaliana. Rhizosphere microorganisms that increased and prolonged N bioavailability by nitrification delayed flowering by converting tryptophan to the phytohormone indole acetic acid (IAA), thus downregulating genes that trigger flowering, and stimulating further plant growth. The addition of IAA to hydroponic cultures confirmed this metabolic network.

Conclusions

We document a novel metabolic network in which soil microbiota influenced plant flowering time, thus shedding light on the key role of soil microbiota on plant functioning. This opens up multiple opportunities for application, from helping to mitigate some of the effects of climate change and environmental stress on plants (e.g. abnormal temperature variation, drought, salinity) to manipulating plant characteristics using microbial inocula to increase crop potential.

Background

Climate change has altered plant phenology [1, 2]. This has crucial biological, physical, and chemical effects on the biosphere and the earth system [3]. These phenological alterations have become a subject of great interest in ecological and environmental sciences. Changes to phenology have been attributed to multiple factors, including warming [4], but the role of plant microbiota and particularly rhizosphere microbiota has not been considered. And yet, the rhizosphere harbors a diverse community of microorganisms that play critical roles in plant growth and reproduction [5, 6].

We know that rhizosphere microbiota protect against pathogens, improve growth by producing phytohormones, and may help plants withstand environmental perturbations such as abnormal variation in temperature, drought, and salinity related to climate [7,8,9,10]. Recent studies also suggest that root microbiota can contribute to phenotypic plasticity, which has important implications for our understanding of plant phenology in a changing climate and for increasing crop production [11, 12]. Several auxins have decisive functions in the establishment of plant developmental and reproductive programs [13, 14]. Auxins can be synthesized by rhizosphere microorganisms [15, 16], raising the intriguing possibility that root microbiota may regulate plant growth and development through phytohormone production.

Understanding the interactions between plant microbiota, root exudation, and plant growth and reproduction, however, remains limited, despite significant advances in the last decade [17]. Root exudates account for 5ā€“21% of total photosynthetically fixed carbon and help drive the composition of rhizosphere communities [18, 19]. Exudates may be excess plant products [20, 21], but they can also contain signaling and chemoattractant molecules. These molecules recruit beneficial microorganisms that contribute to pathogen resistance, water retention, and the synthesis of growth-promoting hormones [22], and may influence plant phenotype [23].

Interactions between exudates, soil microbiota, and plant physiology have the potential to dynamically affect rhizospheric communities and alter plant phenotypes by complex feedback mechanisms. We studied the molecular interactions among root exudates, rhizosphere microbiota, and plant physiology in wild-type (Wt) and mutant (pgr5) plants of Arabidopsis thaliana (hereafter Arabidopsis) and identified a novel network of molecular interactions linking the nitrogen cycle, the phytohormone IAA produced from Tryptophan (Trp), and the timing of flowering. These results thus provide evidence of an outstanding phenomenon: the timing of plant flowering may be influenced by soil microbiota.

Results and discussion

Rhizosphere microbiota can delay the onset of flowering of Wt Arabidopsis

Multiple generations of experimental adaptation/acclimation could be used to observe microbially mediated mechanisms of plant growth and reproduction [24,25,26]. To test whether the multi-generations of rhizosphere microbiota can induce earlier or delay flowering time, we measured the phenotypic parameters of Arabidopsis plants growing in soil for three generations (G1, G2, or G3) inoculated with different soil microbiomes (Fig.Ā 1a). The phenotypic parameters of Wt Arabidopsis did not change significantly in plants treated with microbiota isolated from the roots of wild-type plants (Wt-M treatment) compared to the corresponding control (growing in sterilized soil without addition of soil microbiomes) during the first two generations (AdditionalĀ fileĀ 1: Table S1). This indicates that plants in sterilized soil could grow as well as those grown in sterilized soil inoculated with a live microbial slurry during the first two generations. Wt-M rhizosphere microbiota significantly affected flowering and reproduction by the third generation. Flowering time in the G3-Wt-M group was significantly delayed, by approximately 3ā€‰days, and silique number increased significantly.

Fig. 1
figure 1

Design of the microcosmic experiment across generations and the profiles of rhizosphere microbial communities. a The experimental operation diagram of soil microbiota selection by plants; rhizosphere microbial richness: ACE index and number of species per sample (b); and relative abundance of the 10 most abundant microbial phyla (c) across three generations of Arabidopsis grown in microcosms. G-Wt-M represents microbiota in the corresponding generation of wild-type; G-pgr5-M represents microbiota in the corresponding generation of pgr5 Arabidopsis. Taxonomy details and significance analysis are shown in Additional file 2. Different letters represent significant differences (ANOVA followed by an LSD test; pā€‰<ā€‰0.05). Values are meansā€‰Ā±ā€‰SDs (nā€‰=ā€‰3)

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The richness and diversity of the rhizosphere microorganisms tended to decrease in parallel with the changes in Arabidopsis physiology over the three generations. Species richness and diversity based on four indices (Chao1, abundance-based coverage (ACE), number of species, and the Shannon index) significantly decreased after the two and three generations (Fig.Ā 1b and AdditionalĀ fileĀ 1: Figure S1). The relative abundances of Proteobacteria and Acidobacteria, the dominant bacterial phyla in the rhizosphere, decreased by generations 2 and 3 relative to generation 1. In contrast, Bacteroidetes and cyanobacterial abundances increased by generation 3 (Fig.Ā 1c and AdditionalĀ fileĀ 2). It was demonstrated that some early (or late)-flowering plant could be associated to specific soil microorganism families [25] and that plant microbiota could be associated with changes in different plant growth phases [27]. The results suggest that the selected enriched microbes during the three generations play crucial roles in modulating plant flowering time.

Rhizosphere microbiota advanced the flowering time of the pgr5 mutant

To better understand the relationships between microbiota, exudates, and flowering time, we used an Arabidopsis mutant (for the PGR5 gene that encodes a novel thylakoid membrane protein) that grows as well as Wt plants in the vegetative phase [28, 29]. The pgr5 mutant is deficient in antimycin A-sensitive cyclic flow from ferredoxin to plastoquinone, which is one of the most crucial physiological processes for efficient photosynthesis [28]. Because of defects in photosynthesis, the pgr5 mutant produces different exudates from the Wt Arabidopsis. The phenotype of the pgr5 mutant was unchanged in generations 1 and 2 in the group treated with pgr5 microbiota (pgr5-M) compared to the corresponding control (without the addition of soil microbiomes), as for the Wt Arabidopsis. The flowering time of the pgr5-M-treated group, however, was nearly 4ā€‰days earlier by generation 3, in contrast to Wt, and the silique number was significantly lower (AdditionalĀ fileĀ 1: Table S1). The changes in plant reproduction induced by the microbial manipulations were probably not driven by rhizosphere diversity, because the Shannon and richness indices of the pgr5-M- and Wt-M-treated groups did not generally differ over the three generations (AdditionalĀ fileĀ 1: Figure S1). The ACE data, though, differed after one generation (Fig.Ā 1b). The relative abundances of the phyla differed only marginally between the two Arabidopsis lines in each generation (Fig.Ā 1c).

Rare rhizosphere microbes potentially affected flowering time

The abundances of microbial phyla were relatively constant (see above), but abundances between the WM- (microbiota from the third-generation Wt cultures) and the PM (microbiota from the third-generation pgr5 cultures)-treated groups differed more at lower taxonomic levels. The relative abundances of 77 rhizosphere genera differed significantly between the WM and PM treatment by generation 3, by at least a factor of two. A total of 41 genera were enriched in the WM treatment relative to the PM treatment, and 36 genera were enriched in the PM treatment (AdditionalĀ fileĀ 1: Table S2 and AdditionalĀ fileĀ 3).

Most of the enriched rhizosphere microorganisms were initially rare (relative abundance <ā€‰1%), such as Emticicia, Methylobacterium, and Filimonas, suggesting that rare rhizosphere microbes might play a role in modulating Arabidopsis flowering. Rare microbes can be involved in soil biochemical processes and as active modulators of plant growth and resistance to pathogens [30]. The enriched microbes in the WM treatment mostly have key roles in rhizosphere N regeneration or in maintaining plant growth (AdditionalĀ fileĀ 1: Table S3) [16, 31,32,33,34]. Indeed, Bacillus, enriched in the WM treatment, can potentially contribute to soil N fixation [35]. Potential denitrifying organisms such as Stenotrophomonas and Emticicia, though, were enriched in the PM treatment [31, 36]. We hypothesize that an increase in N fixation and cycling in Wt Arabidopsis associated with the microbiota, and the potential increase in denitrification in the pgr5 mutant, could help increase the duration of N bioavailability in Wt Arabidopsis relative to the pgr5 mutant. Plant pathogenic genera enriched in PM, such as Panacagrimonas and Filimonas, may also contribute to the earlier flowering time, because infected hosts preferentially allocate resources toward reproduction [37, 38]. This hypothesis linking N availability to flowering time is discussed further below within the newly proposed molecular network that modulates flowering time.

Verification of microbial function

We unambiguously demonstrated that flowering time was directly associated with the rhizosphere microbiota. Microbiota from the third-generation pgr5 (PM) or Wt cultures (WM) was used to inoculate cultures of three Arabidopsis lines (Wt and two mutants of the photosynthetic apparatus, pgr5 and pnsB4, deficient in cyclic electron flow from NADPH to plastoquinone) for one generation. The microbiota of the third-generation Wt culture delayed flowering time and increased shoot growth in all cases compared to the treatment using microbiota from the pgr5 cultures. The addition of Wt microbiota delayed flowering by 3.3, 5.5, and 5.7ā€‰days in Wt, the pnsB4 mutant, and the pgr5 mutant, respectively (Fig.Ā 2a). The shoot fresh weight of the plants treated with Wt microbiota also increased significantly in the three lines compared to the treatments with the addition of pgr5 microbiota (Fig.Ā 2b).

Fig. 2
figure 2

Verification of microbial function from the third generation. Number of days to the onset of flowering (i.e., when 80% of the control plants had floral buds of 1ā€‰cm or larger) (a, c) and shoot fresh weight (b, d) in wild-type (Wt) and two mutants (pnsB4 and pgr5) of Arabidopsis grown in microcosms in the presence of unsterilized soil slurry (WM and PM) (a, b) or sterilized soil slurry (WM-S and PM-S) (c, d) from the third generation. WM represents plants with microbiota isolates from wild-type plants in generation 3, PM represents the plants with microbiota isolates from pgr5 plants in generation 3, WM-S represents wild-type Arabidopsis grown with sterilized soil slurry, and PM-S represents Arabidopsis pgr5 mutants grown with sterilized soil slurry. Relative abundance of genes involved in N cycling (e amoA, ammonia oxidation; f nifH, N fixation; g nirK, nitrite reductase; h nosZ, nitrous oxide reductase) in soil samples of Wt and two mutant (pnsB4 and pgr5) lines of Arabidopsis grown in microcosms with the addition of unsterilized rhizosphere soil slurries of wild-type (WM) and mutant (PM) Arabidopsis cultures. Asterisk represents a significant difference between WM and PM (pā€‰<ā€‰0.05). Values are meansā€‰Ā±ā€‰SDs (nā€‰=ā€‰9 with 20 Arabidopsis plants per sample)

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These results clearly indicate that flowering time can be affected by the rhizosphere microbiota. This effect disappeared when the soil slurry was sterilized before inoculation, indicating that heat-stable exudates alone were not modulating Arabidopsis flowering time (Fig.Ā 2c, d). It is interesting that the difference between WM- and WM-S (sterilized soil slurry)-treated plants was not very obvious (AdditionalĀ fileĀ 1: Figure S4). The reason may be that sterilized soil slurry included more N, and other nutrients to influence flowering time, which was in accordance with the results in Fig.Ā 3. Therefore, we speculated that the metabolites in the sterilized slurry also played a role in influencing the flowering time and plant stature.

Fig. 3
figure 3

N availability could be influenced by the addition of microbiota from the third generation. NH4+-N content (A), urease activity (B), NO3āˆ’-N content (C), and nitrate reductase activity (D) after inoculation for the WM- and PM-treated groups in the three Arabidopsis lines (Wt, pnsB4, and pgr5) (nā€‰=ā€‰12). Different letters represent significant differences (pā€‰<ā€‰0.05). The red symbols represent the WM-treated samples, and the blue symbols represent the PM-treated samples

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The addition of the two soil slurries did not change bulk-soil pH, available soil K or P contents (AdditionalĀ fileĀ 1: Table S4), the abundance of key genes involved in the C cycle, or the activities of Ī²-glucosidase or chitinase in the rhizosphere (AdditionalĀ fileĀ 1: Figure S2 and S3) but did affect the abundance of genes (normalized to the abundance of 16S rRNA gene) involved in N cycling (Fig.Ā 2eā€“h) and the amounts of NH4+ (Fig.Ā 3A) and NO3āˆ’ (Fig.Ā 3C) in soil. The concentration of bioavailable N species was generally lower after the addition of the pgr5 microbiota compared to the treatment with the addition of Wt microbiota (Fig.Ā 3A, C). This decrease in N availability in the cultures treated with pgr5 microbiota was accompanied by an increase in the abundance of genes involved in denitrification (nirK and nosZ) and a decrease in the abundance of genes involved in nitrogen fixation (nifH) and nitrification (amoA) compared to the Wt-treated groups (Fig.Ā 2eā€“h). In the Wt-treated group, the activity of urease was higher (Fig.Ā 3B) and nitrate reductase was lower (Fig.Ā 3D) than those in the PM group, which probably resulted in higher NH4+ and NO3āˆ’.

Several lines of evidence support the hypothesis that the rhizosphere microbiota modulated N cycling and bioavailability, leading to N deficiency earlier in the pgr5-treated groups and thus earlier flowering. Flowering can be triggered by low nitrate levels [39], but plants maximize growth before flowering under the conditions of N sufficiency [25].

Different root exudates in the two Arabidopsis lines

Root exudates can act as key substrates or signaling molecules that affect microbial composition [27], so we tested the hypothesis that exudate concentrations and compositions differed between the Arabidopsis lines. A metabolomic analysis found that 34 exudates involved in 10 metabolic pathways were differentially released in the two lines (Wt and pgr5) (see AdditionalĀ fileĀ 1: Table S5, the principal component analysis in Fig.Ā 4a, and ā‰„ā€‰2- or ā‰¤ā€‰0.5-fold changes and p values <ā€‰0.05 in Fig.Ā 4b). Four of the 10 biochemical pathways were upregulated in the Wt cultures relative to the pgr5 cultures (Fig.Ā 4b). Thymine was the most differentially released exudate (AdditionalĀ fileĀ 1: Table S5). Thymine can be degraded by bacteria, perhaps accounting for the increase in NH4+ content in the WM groups (Fig.Ā 3A).

Fig. 4
figure 4

Root exudates of the two Arabidopsis lines. a Principal component analysis (PCA) of root exudates in the Wt and pgr5 treatments (nā€‰=ā€‰6) grown hydroponically. b Differentially released exudates (pā€‰<ā€‰0.05) in the Wt and pgr5 treatments were classified into corresponding metabolic pathways inferred from the KEGG pathway database (nā€‰=ā€‰6). c Tryptophan (Trp) and indole-3-acetic acid (IAA) contents in the soil of the cultures of Wt Arabidopsis or pgr5 mutants grown for three generations in microcosms. d Trp and IAA contents in the soil-cultured Wt Arabidopsis for one generation that had been in advance added the microbiota from the Wt (WM) or the pgr5 mutant (PM) Arabidopsis. Red and blue bars indicate that the exudates for a given pathway are mainly up- or downregulated, respectively, in the Wt cultures relative to the pgr5 mutant cultures. The blue and red vertical dashed lines depict pā€‰=ā€‰0.05 (āˆ’log (0.05)ā€‰=ā€‰1.3) and pā€‰=ā€‰0.01 (āˆ’log (0.01)ā€‰=ā€‰2), respectively. Asterisk represents a significant difference (pā€‰<ā€‰0.05). Values are meansā€‰Ā±ā€‰SDs (nā€‰=ā€‰6)

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Trp and its derivatives, phenols, and some carboxylic acids were preferentially exuded in the Wt cultures (AdditionalĀ fileĀ 1: Table S5). The concentrations of amino acids were generally higher in the Wt cultures, consistent with a higher abundance of Bacillus subtilis in the Wt cultures, for which amino acids are chemoattractants. These metabolomic results are consistent with the hypothesis that differences in exudates affect rhizosphere microbiota [40].

IAA delayed flowering time by downregulating genes involved in flowering

Auxins regulate plant growth in many ways [13, 41, 42]. One of the important auxins for plants is IAA, which is soluble in aqueous solutions and, when protonated, diffuses passively across cell membranes without the need of a specific transporter [43]. IAA has also been hypothesized to have a floral-inductive signaling role by regulating multiple aspects of embryonic and postembryonic development [44, 45]. Microorganisms can produce IAA from Trp [46,47,48,49]. One of the enriched rhizosphere microorganisms, Arthrobacter (AdditionalĀ fileĀ 1: Table S3), has been reported to be beneficial for plant growth by having the ability to produce IAA [16]. Trp and its derivatives were enriched in the Wt exudates, so the generation of IAA by microorganisms may control flowering time by a novel molecular network. Trp content in the soil of generation 3 of the Wt cultures decreased, and the IAA content increased 3.03-fold, suggesting that the Wt microbiota rapidly converted Trp into IAA (Fig.Ā 4c, d).

We explored the possibility that microbially generated IAA delayed flowering time by adding Trp, 5-hydroxytryptophan (5-HTP), and IAA to the hydroponic cultures and monitoring the flowering time of each line. Adding 5 and 25ā€‰nM IAA decreased the bolting proportion of Wt Arabidopsis by 20ā€“30% (Fig.Ā 5a) when 80% of the control plants had floral buds, implying that IAA was the direct driver that delayed flowering time. Changes in the expression of genes involved in flowering further supported the role of IAA in regulating flowering time (Fig.Ā 5b). IAA treatment induced changes in the relative transcription rates of genes associated with flowering. The rates for some of the genes comprising the autonomous, GA, and vernalization pathways changed significantly, and these changes were observable at the early (when 10% of control plants had floral buds), intermediate (when >ā€‰50% of control plants had floral buds), and late (when >ā€‰80% of control plants had floral buds) stages of flowering. The downregulation of gene activity was most consistent in the photoperiod pathway, where multiple genes were downregulated at all flowering stages.

Fig. 5
figure 5

IAA delayed flowering time by downregulating genes involved in flowering. a Proportion of bolting (i.e., percentage of plants had floral buds of 1ā€‰cm or larger). Plants were hydroponically grown in MS medium containing 5ā€‰nM and 25ā€‰nM IAA. b Relative rates of transcription of genes involved in flowering in Wt Arabidopsis at the early, intermediate (Int.), and late stages of flowering after one generation of culture. Plants were hydroponically grown in MS medium containing 5ā€‰nM IAA. All transcription levels are normalized to that of a housekeeping gene (actin 2). Values are meansā€‰Ā±ā€‰SDs (nā€‰=ā€‰6). Asterisk represents a significant difference (pā€‰<ā€‰0.05)

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Shimada et al. [14] reported that IAA relieved the inhibitory effects of aspterric acid on pollen growth and thus speculated that IAA accelerated reproductive growth in Arabidopsis. To our knowledge, our microcosm study is the first to demonstrate that IAA is one critical signal that delays flowering in Arabidopsis, although Wagner et al. [50] also found a similar phenomenon, while not proposing any related mechanism.

Combined with earlier reports, the weight of evidence suggests that IAA stimulates the development of floral organs but delays the flowering time of Arabidopsis. Our data strongly suggest that IAA delays flowering and acts as a signal of optimal growth conditions in the absence of N limitation for growth.

Conclusions

Identifying the community/function relationships for rhizosphere microorganisms and their interaction with plant physiology is critical for determining the role of the plant microbiome in regulating biogeochemical cycles, plant growth, and phenology (Fig.Ā 6). We identified a novel metabolic network in which exudates affect plant rhizosphere microbiota, which can then modulate flowering time by IAA production and can also affect vegetative growth by influencing N availability. IAA-promoted plant growth is expected to further stimulate exudation and hence retroactively affect flowering time in a positive feedback mechanism. Our results have important implications for our understanding and modeling of plant phenology and are of great interest for the biotechnology sector seeking to increase crop potential.

Fig. 6
figure 6

Schematics of interactions between plants and rhizosphere microbiota. The proposed community/function relationships for rhizosphere microorganisms and their interaction with plant physiology and floral phenology through root exudates, N cycling, and production of the phytohormone IAA

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Methods

Seedling culture

Arabidopsis seeds (wild-type Col-0 (Wt) and the pgr5 mutant, deficient in PGR5-dependent cyclic electron flow from ferredoxin to plastoquinone), were surface sterilized to avoid bacterial contamination on solid medium and vernalized as described by Sun et al. [51]. Given that photosynthesis is the main resource of exudates, photosystem mutant with the same genetic background with that of Wt was selected to induce different exudates. Vernalized seeds were cultured in Petri dishes containing Murashige and Skoog (MS) medium under sterile conditions at 25ā€‰Ā°C at a light intensity of 300ā€‰Ī¼mol photons/m2/s and a 12:12-h light to dark photoperiod. The MS medium containing 3% sugar and 0.5% agar was autoclaved at 115ā€‰Ā°C for 30ā€‰min before use. Two-week-old aseptic seedlings were transplanted into polycarbonate pots (400ā€‰mL) containing autoclaved potting-mix soil (Sun Gro Horticulture, MA, USA).

Microcosm experiments across generations

Approximately 30ā€‰g of grassland soil collected near the Zhejiang University of Technology, China (30Ā° 17ā€² 45.11ā€³ N, 120Ā° 09ā€² 50.07ā€³ E) was mixed with 200ā€‰mL of sterile water by vigorous shaking for 60ā€‰s [25]. Ten-milliliter samples of soil slurry were added to polycarbonate pots transplanted with 20 seedlings of either the Wt or the pgr5 Arabidopsis line. Nine replicate pots were used for generation 1 for each line and for a control treatment (nā€‰=ā€‰9) without added soil slurry. Plants grew in an artificial greenhouse at 25ā€‰Ā±ā€‰0.5ā€‰Ā°C and 80% relative humidity under cool-white fluorescent light (300ā€‰Ī¼mol photons/m2/s) with a 12:12-h light to dark cycle.

The plants and soils were harvested when 80% of the plants had floral buds of 1ā€‰Ā±ā€‰0.1ā€‰cm or larger (measured from the center of the rosette), and the time to flowering was recorded. Large soil aggregates that were loosely bound to the roots were first removed by shaking, and 30ā€‰g of the tightly bound rhizosphere soil was then collected (see the ā€œCollection of rhizosphere soilā€ section) and added to 200ā€‰mL of sterile water, producing a soil slurry for generation 1. This slurry was used for inoculating the Arabidopsis lines for the second and third generations, as described above. Treatments inoculated with the microbiota of Wt and the pgr5 mutant were designated WM and PM, respectively. The generations in our study refer to the propagation of soil microbes only, and all seeds were from a common stock. At flowering stage and harvest time, the physiological parameters including the number of days before flowering, fresh weight, number of rosette leaves, and number of siliques were determined in wild-type (Wt) and pgr5 mutant ecotypes grown in microcosms for each generation.

Collection of rhizosphere soil

Rhizosphere soil was collected as described by Bulgarelli et al. [9]. Four-centimeter sections of roots were collected immediately below the rosette, and the roots from each pot were transferred to a 50-mL centrifuge tube containing 20ā€‰mL of sterile phosphate buffer saline (PBS; 137ā€‰mM sodium chloride, 10ā€‰mM phosphate buffer, 2.7ā€‰mM potassium chloride; pHā€‰7.3ā€“7.5). The centrifuge tubes were shaken at 40ā€‰g for 20ā€‰min on an orbital shaker. The roots were removed, the solution was centrifuged at 1000g for 20ā€‰min, and the pellet of rhizosphere soil was recovered. All samples of rhizosphere soil were frozen in liquid nitrogen and stored at āˆ’ā€‰80ā€‰Ā°C until analysis.

16S rRNA gene sequencing

The frozen soil samples were thawed on ice, and DNA was extracted using a PowerSoil DNA Isolation Kit (MO BIO Laboratories, Inc., Carlsbad, USA). 16S rRNA genes were amplified using EXtaq enzyme (TaKaRa, Kyoto, Japan) and the specific primers 314F (5ā€²-CCTACGGGNGGCWGCAG-3ā€²) and 805R (5ā€²-GACTACHVGGGTATCTAATCC-3ā€²) with the adapter (index) that targets the V3 and V4 variable regions of bacterial/archaeal 16S rRNA genes. Strongly amplified products 460ā€‰bp in length were chosen for further experiments. The amplicons were quantified with a Qubit 2.0 fluorometer (Thermo Fisher Scientific, USA), diluted to 1ā€‰ng/Ī¼L, and sequenced on a MiSeq platform (PE250). In total, 854,514 raw reads were obtained from the 18 samples of rhizosphere soils (6 groups as shown in Fig.Ā 1a, nā€‰=ā€‰3). We computed operational taxonomic units (OTU) and microbial diversity as described previously [52]. Rarefaction curves of observed species are shown in AdditionalĀ fileĀ 1: Fig. S5.

Analysis of rhizosphere DNA abundance by quantitative real-time PCR (qRT-PCR)

Rhizosphere DNA was quantified by ultraviolet-visible spectrophotometry (ND 5000, BioTeke, China) and diluted to 10ā€‰ng/Ī¼L. The abundances of rhizosphere genes (amoA, nifH, nirK, nosZ, cbbL, Ī²-glu, and ChiA; AdditionalĀ fileĀ 1: Table S6) were measured in 10-Ī¼L PCRs containing 5ā€‰Ī¼L of SYBR Green Real-time PCR Master Mix (Toyobo, Tokyo, Japan), 0.4ā€‰Ī¼L of each of the forward and reverse primers (10ā€‰mM) (see AdditionalĀ fileĀ 1: Table S6 for a list of primers), 1ā€‰Ī¼L of rhizosphere DNA at 10ā€‰ng/L, and 3.2ā€‰Ī¼L of ddH2O. The qRT-PCR protocol was 94ā€‰Ā°C for 3ā€‰min followed by 40ā€‰cycles of 94ā€‰Ā°C for 30ā€‰s, 56ā€‰Ā°C for 30ā€‰s, and 72ā€‰Ā°C for 1ā€‰min on an Eppendorf MasterCycler ep RealPlex (Wesseling-Berzdorf, Germany).

Measurements in the dissolved phase of the soil samples

Physicochemical (nutrient contents and pH) and biological (enzymatic activities and concentrations of IAA and Trp) variables were measured in the dissolved phase of the soil samples. After three generations of Arabidopsis cultures (Fig.Ā 1a), soil samples were then collected randomly from each pot, air-dried, homogenized, and sieved to obtain particles <ā€‰1ā€‰mm. The activity of soil enzymes (Ī²-glucosidase, chitinase, urease, and nitrate reductase) and soil N content (NH4+ and NO3āˆ’ contents) were subsequently measured using 0.5ā€‰g of soil (nā€‰=ā€‰4) following the manufacturerā€™s instructions of corresponding commercial reagent kits (COMIN, Suzhou, China). The concentrations of two key metabolites (IAA and Trp) were measured in the soil dissolved phase. Five grams of soil was mixed with 5ā€‰g of NaCl and 20ā€‰mL of acetonitrile for 5ā€‰min, followed by centrifugation at 1000g for 10ā€‰min. The concentrations of IAA and Trp in the supernatants were measured by Liquid Chromatography-Electrospray Ionization-Mass/Mass Spectroscopy (LC-ESI-MS/MS, Q-Trap 5500, Agilent Technologies, USA).

Collection, measurement, and identification of root exudates

Arabidopsis seedlings (Wt and pgr5 mutant) reached the bolting stage after approximately 40ā€‰days of culture and were then transferred to glass containers containing 40ā€‰mL of ddH2O [27]. After 3ā€‰days of culture in the glass containers, culture media containing exudates were passed through 0.45-Ī¼m filter membranes. Approximately 35ā€‰mL of the solution was freeze-dried, dissolved in 500ā€‰Ī¼L of 80% methanol, and derivatized with Bis (trimethylsilyl) trifluoroacetamide and 1% chlorotrimethylsilane. The derivatized samples were analyzed by gas chromatography/mass spectroscopy GC-MS (Agilent 7890B gas chromatographic system coupled to an Agilent 5977A Mass Spectrometry Detector (Agilent, USA)). The potential involvement of all identified exudates in Arabidopsis biochemical pathways was subsequently determined by reference to the KEGG database [52].

Addition of Trp, 5-hydroxytryptophan (5-HTP), and IAA and analysis of gene transcription associated with flowering

For hydroponic experiments (i.e., plants cultured in solution), Trp, 5-HTP, and IAA were added to autoclaved liquid MS medium cultured with Wt at final concentrations of 0.5, 5, and 25ā€‰nM, respectively. Control cultures without Trp, 5-HTP, and IAA were performed in parallel. The transcription of genes involved in flowering was measured by qRT-PCR. Control groups treated with Trp, 5-HTP, and IAA were analyzed at three stages of development: (1) early flowering (when 10% of control plants had floral buds), (2) intermediate flowering (when >ā€‰50% of control plants had floral buds), and (3) late flowering (when >ā€‰80% of control plants had floral buds) stages. Total RNA was isolated from the plants and then reverse transcribed into cDNA for qRT-PCR analysis using the protocol described by Chen et al. [11] and the primer pairs in AdditionalĀ fileĀ 1: Table S6. We studied the transcription of six genes in the autonomous pathway (FCA, FLD, FPA, FVE, FY, and LD), three genes in the gibberellin acid (GA) pathway (GAI, GA1, and RGA), six genes in the vernalization pathway (FR1, VRN1, VRN2, VIN3, and PIE1), five genes in the photoperiod pathway (CCA1, CO, GI, LHY, and TOC1), and five genes in the floral integrator pathway (FLC, FT, SOC1, AGL-24, LFY, and AP1).

Data analysis and statistical methods

For the biochemical and physiological measurements, analysis of variance followed by the Dunnettā€™s post hoc test was performed to evaluate the statistical significance among data using the StatView 5.0 program (Statistical Analysis Systems Institute, Cary, NC, USA). Means among treatments were considered significantly different, when the probability (p) was less than 0.05. All analyses were performed in triplicate unless otherwise stated. All data are presented in the tables and figures as meanā€‰Ā±ā€‰SD (standard deviation).

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Acknowledgements

We sincerely thank all the authors who provided valuable data or comments for this study. We are very thankful to Dr. Tsuyoshi Endo and Professor Fumihiko Sato (Kyoto University, Japan) who provided the pnsB4 and pgr5 mutant lines of Arabidopsis thaliana.

Funding

This work was financially supported by the National Natural Science Foundation of China (21577128, 21777144), the Strategic Priority Research Program of the Chinese Academy of Sciences (XDB15020302 and XDB15020402), the CAS Pioneer Hundred Talents Program (H.F. Qian), and the Xingjiang Uighur Autonomous Region Talent Project (H.F. Qian). JP research is funded by the European Research Council Synergy grant SyG-2013-610028 IMBALANCE-P.

Availability of data and materials

All data needed to evaluate the conclusions in the paper are present in the paper and/or the supplementary materials. The raw data of 16S rRNA gene sequences have been submitted to the NCBI Sequence Read Archive (SRA) database under the BioProject number PRJNA494813.

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Author notes

  1. Tao Lu and Mingjing Ke contributed equally to this work.

Authors and Affiliations

  1. College of Environment, Zhejiang University of Technology, Hangzhou, 310032, Peopleā€™s Republic of China

    Tao Lu,Ā Mingjing Ke,Ā Yujian Jin,Ā Xiaoji Fan,Ā Zhenyan Zhang,Ā Liwei SunĀ &Ā Haifeng Qian

  2. Quebec-Ocean and Takuvik Joint International Research Unit, UniversitƩ Laval, QuƩbec, G1VOA6, Canada

    Michel Lavoie

  3. College of Biotechnology and Bioengineering, Zhejiang University of Technology, Hangzhou, 310032, Peopleā€™s Republic of China

    Zhengwei Fu

  4. Department of Biological Sciences, Macquarie University, Sydney, NSW, 2109, Australia

    Michael Gillings

  5. CSIC, Global Ecology Unit, CREAF-CSIC-UAB, Barcelona, Catalonia, Spain

    Josep PeƱuelas

  6. CREAF, Cerdanyola del VallĆØs, Barcelona, Catalonia, Spain

    Josep PeƱuelas

  7. Xinjiang Key Laboratory of Environmental Pollution and Bioremediation, Xinjiang Institute of Ecology and Geography, Chinese Academy of Sciences, Urumqi, 830011, Peopleā€™s Republic of China

    Haifeng Qian

  8. Key Lab of Urban Environment and Health, Institute of Urban Environment, Chinese Academy of Sciences, Xiamen, 361021, Peopleā€™s Republic of China

    Yong-Guan Zhu

  9. State Key Lab of Urban and Regional Ecology, Research Center for Ecoenvironmental Sciences, Chinese Academy of Sciences, Beijing, 100085, Peopleā€™s Republic of China

    Yong-Guan Zhu

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  1. Tao Lu
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Contributions

HFQ, ZWF, and YGZ designed the study; TL, MJK, YJJ, XJF, and ZYZ performed the research; HFQ, TL, MJK, YJJ, LWS, and YGZ analyzed the data; and HFQ, TL, YJJ, ML, MG, JP, and YGZ wrote the manuscript. All authors read and approved the final manuscript.

Corresponding authors

Correspondence to Haifeng Qian or Yong-Guan Zhu.

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Additional files

Additional file 1:

Figure S1. Rhizosphere microbiota richness and diversity. Figure S2. Abundance of carbon cycle-related genes in rhizosphere soil. Figure S3. Activities of carbon cycle-related enzymes in rhizosphere soil. Figure S4. Comparisons between WM- and WM-S-treated plants. Figure S5. Rarefaction curves of observed species. Table S1. Physiological parameters of Arabidopsis in three generations. Table S2. Significant enrichment of rhizosphere microorganisms in the third generation. Table S3. nriched rare microorganisms in Wt and pgr5 Arabidopsis. Table S4. Bulk soil properties measured after addition of WM and PM soil slurries. Table S5. Comparison of root exudates between Wt and pgr5 mutant Arabidopsis. Table S6. Sequences of the primer pairs used for qRT-PCR. (DOCX 348 kb)

Additional file 2:

Taxonomy (relative abundance) of rhizosphere microorganisms at the phylum level. (XLSX 35 kb)

Additional file 3:

Taxonomy (relative abundance) of rhizosphere microorganisms at the genus level. (XLSX 46 kb)

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Lu, T., Ke, M., Lavoie, M. et al. Rhizosphere microorganisms can influence the timing of plant flowering. Microbiome 6, 231 (2018). https://doi.org/10.1186/s40168-018-0615-0

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Keywords

Microbiome

ISSN: 2049-2618

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