Microbes and Environments
Online ISSN : 1347-4405
Print ISSN : 1342-6311
ISSN-L : 1342-6311
Short Communication
Effects of Different Types of Additional Fertilizers on Root-associated Microbes of Napa Cabbage Grown in an Andosol Field in Japan
Seishi IkedaKazuyuki OkazakiHirohito TsurumaruTakanori SuzukiMasayuki Hirafuji
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2022 年 37 巻 2 号 論文ID: ME22013

詳細
Abstract

The effects of different types of additional fertilizations (a compound fertilizer and Chiyoda-kasei) on the root-associated microbes of napa cabbage grown in an Andosol field were investigated by molecular community ana­lyses. Most of the closest known species of the bacterial sequences whose relative abundance significantly differed among fertilizers were sensitive to nitrogen fertilization and/or related to the geochemical cycles of nitrogen. The fungal community on the roots of napa cabbage was dominated by two genera, Bipolaris and Olpidium. The relative abundance of these two genera was affected by the types of fertilizers to some extent and showed a strong negative correlation.

An understanding of the diversity and functionality of environmental microbes is a key factor for constructing a sustainable agricultural system as a green technology (Bulgari et al., 2019). However, the practical utilization of the functionality of beneficial microbes remains challenging (Raymaekers et al., 2020). One of the main reasons for this is most likely due to the lack of sufficient information on the interactions between beneficial microbes and diverse environmental factors, including fertilizers and pesticides (Ikeda et al., 2010a). The impact of basal and additional fertilizations on plant-associated microbes has been assessed in the last decade (Ikeda et al., 2010b, 2011, 2015; Rodríguez-Blanco et al., 2015; Beltran-Garcia et al., 2021; Wang et al., 2022); however, the effects of qualitative differences in additional fertilizations remain unknown.

In contrast to a basal fertilizer, which is thoroughly mixed into soil at the beginning of cultivation, an additional fertilizer is often applied to the soil surface (top dressing fertilization). Chiyoda-kasei (SUN AGRO) is a unique fertilizer that is expected to have high solubility and rapid diffusibility from the surface of a field into soil, which is most likely due to its porous structure (Fig. S1A). By reacting liquid and gas in its production processes, each of the chemical components in a particle of Chiyoda-kasei is more evenly distributed within its particles than in a general compound fertilizer (Fig. S1A and B). These unique features of Chiyoda-kasei are advantageous for top dressing with an additional fertilization because they support the fast growth of crops with a rapid and balanced nutrient supply to soil. Therefore, Chiyoda-kasei may also have a unique impact on plant-associated microbes over a conventional compound fertilizer. The present study investigated the root-associated microbes of napa cabbage after top dressing with an additional fertilizer using Chiyoda-kasei and a conventional compound fertilizer.

The seeds of the napa cabbage (Brassica rapa var. pekinensis) cultivar “Kigokoro85” (Takii & Co.) were sown in a seedling cultivation cell tray (vegetable tray [25×25‍ ‍mm, 200 cells]; Yanmar Holdings) under greenhouse conditions on September 9, 2020 and grown for 31 days. Takii cell baido TM-1 (Takii & Co.) was used as the planting soil (3 L tray–1). Seedlings were planted in CO and CK plots fertilized with a compound fertilizer and Chiyoda-Kasei, respectively, in an experimental field (light-colored Andosol, 36°01′07″N, 139°41′27″E, 9.4 m a.s.l.) (Shiraoka). Inter-row and intra-row distances were 60 and 40‍ ‍cm, respectively. Row lengths were both 10 m for the CO and CK plots (24 m2 in size), and planting was performed on October 6, 2020.

A basal fertilization (140‍ ‍kg of N ha–1, 140‍ ‍kg of P2O5 ha–1, and 140‍ ‍kg of K2O kg ha–1, a compound fertilizer) was applied to the CO and CK plots at the time of planting. Seedlings and rows were covered with a mulching film (L-L strengthened Sankyo mulch, dark green, thickness of 0.02‍ ‍mm, width of 95‍ ‍cm; Sankyo). A compound fertilizer (60‍ ‍kg of N ha–1 [93% ammonia nitrogen {w/w} and 7% urea {w/w}], 60‍ ‍kg of P2O5 ha–1, and 60‍ ‍kg of K2O kg ha–1) and Chiyoda-kasei (60‍ ‍kg of N ha–1 [100% ammonia nitrogen {w/w}], 60‍ ‍kg of P2O5 ha–1, and 40‍ ‍kg of K2O kg ha–1) were used as additional fertilizations for the CO and CK plots, respectively. Additional fertilizations were applied twice to the soil surface of each plot, 20 to 30‍ ‍cm from a plant under a mulch film, on October 26 and November 17, 2020.

The short diameters of 22 and 24 heads of napa cabbage were measured for the CO and CK plots, respectively, on November 5, 2020. Growth parameters (the weight of all above-ground tissue, the head, and outer leaves, and the ratio to head weight) were examined for 10 plants randomly selected from each of the CO and CK plots on December 18, 2020. Head weight was calculated as follows: (weight of all above-ground tissue)–(weight of the outer leaves). The ratio to head weight was calculated as follows: (head weight) (weight of all above-ground tissue)–1×100. Based on the head weight, four representative heads from 10 plants described above were selected from each of the CO and CK plots and the corresponding roots of 4 plants per plot were carefully dug up as replicates for DNA extraction on December 18, 2020. After serially washing and rinsing roots with tap and sterilized water, roots were stored at –30°C until used for DNA extraction.

The roots of individual plants were grounded in liquid nitrogen with a mortar and pestle. A portion of a pulverized sample (0.4 g) was transferred to a Lysing Matrix E tube (MP Biomedicals), and a DNA sample was prepared as described in a previous study (Ikeda et al., 2004), except that a homogenizer (FastPrep®24, MP Biomedicals) was used for the bead-beating step (5.5 ms–1 at room temperature for 30 s) and a DEAE-cellulose column treatment was omitted. Pelleted DNA was then washed with 70% ethanol and suspended in 100‍ ‍μL of TE buffer (pH 7.6).

To conduct a community ana­lysis of napa cabbage root-associated bacteria and fungi, PCR amplification of the V3–V4 region of the bacterial 16S rRNA gene and the partial sequence of the internal transcribed space in the fungal rRNA gene region, sequencing with a MiSeq sequencer (Illumina), and sequence editing with Qiime (Caporaso et al., 2010) and Qiime2 (Bolyen et al., 2019) were conducted at the Bioengineering Lab prior to statistical ana­lyses, as summarized in the supplementary materials. Statistical ana­lyses were performed using JMP software version 12 (SAS Institute). Raw reads used in the present study were deposited into the NCBI SRA database (BioProject accession number: PRJNA718730).

The short diameter of the head, the weight of all above-ground tissue, head weight, and the ratio to head weight were significantly higher in the CK plot than in the CO plot (Table 1). The results of soil chemical ana­lyses showed that ammonia nitrogen was 3-fold higher in the CK plot than in the CO plot, suggesting the high diffusibility of nitrogen from the surface of the field into soil in the CK plot (Table S1). No significant differences were observed in any diversity indexes between the CO and CK plots (Table S2).

Table 1. Comparisons of growth parameters of napa cabbage heads between compound fertilizer and Chida-kasei plots
Fertilization plotsa Short
diameter
of the head
(cm)
Weight of all
above-ground
tissue
(kg plant–1,
n=10)
Head weight
(kg plant–1,
n=10)b
Weight of outer
leaves
(kg plant–1,
n=10)
Ratio to head
weight
in above-ground
tissue
(%, n=10)c
CO 52 (n=22) 2.52 1.57 0.95 62.2
CK 55** (n=24) 2.83* 1.97*** 0.86 69.5**

a CO and CK indicate the compound fertilizer and Chiyoda-kasei plots, respectively.

b (Weight of all above-ground tissue)–(Weight of outer leaves).

c (Head weight) (Weight of all above-ground tissue)–1×100.

*, **, and *** indicate a significant difference with a t-test at P<0.05, P<0.01, and P<0.001, respectively.

All traits were examined on December 18, 2020, except for the short diameter of the head, which was measured on November 5, 2020.

Taxonomic ana­lyses of bacterial sequence data identified 20 phyla, 50 classes, 82 orders, 129 families, 200 genera, and 217 species. A clustering ana­lysis of bacterial sequence data with 100% identity generated 574 ASVs. Among these taxa and ASVs, 10 taxa and 5 ASVs were identified as bacterial groups that were significantly less abundant in the CK plot than in the CO plot (Table 2). Most of the closest known bacterial groups of these taxa and ASVs were previously reported to be sensitive to nitrogen fertilization and/or related to the geochemical cycles of nitrogen. Caulobacteraceae and Thermomonosporaceae were previously shown to reduce their abundance in response to an increase in nitrogen fertilization in the rhizosphere soil of canola (B. napus) (Monreal et al., 2018). Caulobacteraceae and Chitinophagaceae increased their abundance in the rhizosphere soil and roots of Triticum aestivum under nitrogen starvation conditions (Pagé et al., 2019). The direct application of nitrate to soil decreased the abundance of Caulobacteraceae in Arabidopsis roots (Konishi et al., 2017). Collectively, these findings suggest that Caulobacteraceae favors a low soil nitrogen level. Caulobacter and Chitinophagaceae have both been recognized as beneficial bacterial groups (Madhaiyan et al., 2015; Luo et al., 2019), and may not be competitive in a rhizosphere under a high soil nitrogen level.

Table 2. Bacterial groups showing significant differences in relative abundance between compound fertilizer and Chiyoda-kasei plots
Taxona Relative abundance (%)b Fold change
(CK/CO)
COc CK
Class
Alphaproteobacteria 14.66±0.68 12.66±1.18* 0.86
Planctomycetia 0±0 0.09±0.09*
Order
Rhizobiales 7.72±0.32 6.76±0.64* 0.88
Spirobacillales 0.05±0.03 0±0*
Sva0725 0.27±0.22 0.04±0.09* 0.16
Family
Caulobacteraceae 4.11±0.36 3.37±0.41* 0.82
Unclassified Legionellales 0.09±0.09 0.33±0.10* 3.55
Thermomonosporaceae 0.19±0.16 0±0*
Genus
Caulobacter 3.26±0.18 2.56±0.26** 0.79
Kribbella 0.22±0.23 0±0*
Rubrivivax 1.61±0.82 0.37±0.67* 0.23
Species
Unclassified Caulobacter 1.53±0.37 0.92±0.16* 0.60
ASVd
 ASV-B1 (Chitinophagaceae) 0.24±0.11 0.06±0.07* 0.25
ASV-B2 (Chitinophaga) 0.16±0.24 0.91±0.26* 5.58
 ASV-B3 (Niastella) 0.84±0.61 0±0*
ASV-B4 (Sphingobacteriales) 0±0 0.51±0.05***
 ASV-B5 (Comamonadaceae) 1.00±0.90 0±0*
ASV-B6 (Comamonadaceae) 0.18±0.36 0.68±0.13* 3.81
ASV-B7 (Ellin6067) 0±0 0.16±0.12*
ASV-B8 (Methylotenera mobilis) 0±0 0.20±0.16*
 ASV-B9 (Myxococcales) 0.28±0.21 0±0*
ASV-B10 (Legionellales) 0.07±0.10 0.33±0.10* 4.88
 ASV-B11 (Dokdonella) 1.08±0.11 0.77±0.14* 0.71

a When the same value for relative abundance was obtained at different taxonomic levels for a bacterial group, only the lowest taxonomic group was shown. Bacterial groups showing a higher abundance in the CK plot than in the CO plot are shown in bold font.

b Relative abundance (%) is calculated based on 2,927 reads per sample and the results of the average and S.D. (n=4) for each of the fertilization conditions are shown.

c CO and CK indicate the compound fertilizer and Chiyoda-kasei plots, respectively.

d The closest taxon to a representative sequence of an ASV is shown in parentheses.

*, *, and *** indicate a significant difference between the CO and CK plots at P<0.05, P<0.01, and P<0.001, respectively.

Kribbella and Niastella (corresponding to ASV-B3 in Table S3) have been identified as a nitrate reducer and denitrifier, respectively (Nishizawa et al., 2014; Ozdemir-Kocak et al., 2017). Increases in the abundance and activities of these bacteria in a rhizosphere are not favorable from the viewpoint of agriculture because their effects on mineral nitrogen may reduce the efficiency of nitrogen fertilization. Niastella has also been reported as a bacterial group associated with the roots of sugarcane with relatively high abundance, and a root-associated OTU belonging to this genus was enriched under lower nitrogen fertilization than the standard level (Yeoh et al., 2016). Rubrivivax is a nitrogen fixer (Willems et al., 1991) and is likely to be less competitive in nitrogen-rich environments. Variovorax (corresponding to ASV-B5 in Table S3) is a well-known beneficial bacterial group that exerts plant growth-promoting (PGP) effects on diverse plants, including Brassica species (Bertrand et al., 2001; Natsagdorj et al., 2019; Okazaki et al., 2021). An ASV belonging to Variovorax was previously shown to be enriched in the roots of wheat under low nitrogen fertilization (Pagé et al., 2019). Furthermore, Dokdonella (corresponding to ASV-B11) decreased its abundance under high nitrogen fertilization (Shang and Yi, 2015).

As bacterial groups that were more abundant in the CK plot than in the CO plot, 2 taxa and 6 ASVs were identified (Table 2). Although root-Legionellales interactions remain largely unknown, regarding nitrogen fertilization, Zhou et al. (2015) reported that the relative abundance of Legionellales positively correlated with nitrogen fertilization and wheat yield. They also linked their abundance to the high yield of wheat, which was associated with the high capability for ammonium assimilation by members of Legionellales (Vishnivetskaya et al., 2013). Consistent with these findings, the high abundance of unclassified Legionellales in the CK plot appeared to be attributed to responses to the high concentration of ammonia nitrogen in the CK plot (Table S1). Chitinophaga filiformis (corresponding to ASV-B2 in Table S3) is a chitinolytic bacterium (Kämpfer et al., 2006) that may be antagonistic to fungal groups such as Bipolaris, which has chitin as the main component of the cell wall. The responses of Sphingobacteriales to fertilization have been examined in studies using community ana­lyses. Sapp et al. (2015) showed that the relative abundance of some OTUs belonging to Sphingobacteriales positively or negatively correlated with N and P fertilizers at the OTU level. In a study by Ling et al. (2017), the relative abundance of Sphingobacteriales negatively and positively correlated with nitrogen and phosphate fertilization, respectively, at the order and genus levels. These findings suggest that each bacterial group of Sphingobacteriales may respond differently to fertilization input at lower taxonomic levels. In the present study, the taxonomic affiliation of ASV-B4 (Sphingobacteriales) at a lower taxonomic level was unclear, as shown in Table S3, and, thus, difficulties are associated with comparisons with previous studies and obtaining insights for future research.

Pelomonas (corresponding to ASV-B6 in Table S3) is a root-associated diazotroph (Xie and Yokota, 2005) that has also been identified as an endophytic bacterial group for rapeseed (Glaeser et al., 2020). Methylophilaceae (corresponding to ASV-B8 in Table S3) has been reported to link methanol oxidation to denitrification in freshwater lake sediment. Previous studies demonstrated the emission of methanol from roots as a byproduct of active growth (Sy et al., 2005) and the colonization of methanol-utilizing bacteria, such as Methylobacterium species, on roots (Poonguzhali et al., 2008). The presence of ASV-B8 only in the CK plot may reflect the dominance of a unique bacterial group that assimilates methanol derived from actively growing roots in the CK plot in a nitrate-dependent manner.

Taxonomic ana­lyses of fungal sequence data identified 6 phyla, 9 classes, 26 orders, 49 families, and 64 genera. These results revealed that the sum of the relative abundance of Bipolaris and Olpidium was more than 90% for all samples examined. A clustering ana­lysis of fungal sequence data with 97% identity generated 419 OTUs. A total of 318 OTUs (75.9%) were counted for Bipolaris sp. and their abundance ranged between 0 and 50% at the individual plant level. As fungal groups that were significantly less abundant in the CK plot than in the CO plot, 5 taxa and 18 OTUs (all belonging to Bipolaris) were identified (Table 3). A phylogenetic ana­lysis revealed that 18 OTUs in Table 3 were largely classified into 3 groups (Fig. S2). In addition, a strong negative correlation was observed between the relative abundance of Bipolaris- and Olpidium-related taxa from the phylum to OTU levels (Fig. 1). Correlation ana­lyses at the OTU level further revealed that the relative abundance of one dominant (OTU-F13) and 34‍ ‍minor OTUs in the genus Bipolaris negatively correlated with that of OTU-F20 (Olpidium) (Table S4).

Table 3. Fungal groups showing significant differences in relative abundance between compound fertilizer and Chiyoda-kasei plots
Taxona Relative abundance (%)b Fold change
(CK/CO)
COc CK
Family
Pleosporaceae 83.9±8.6 50.5±13.0** 0.60
Xylariaceae 0±0 0.12±0.09*
Genus
Bipolaris 83.5±8.6 50.2±13.3** 0.60
Olpidium 9.1±10.0 43.9±15.4** 4.84
OTUd
 OTU-F1 (Bipolaris) 1.60±0.29 0.97±0.35* 0.61
 OTU-F2 (Bipolaris) 0.47±0.12 0.26±0.10* 0.55
 OTU-F3 (Bipolaris) 0.63±0.10 0.26±0.05*** 0.40
 OTU-F4 (Bipolaris) 0.82±0.24 0.43±0.18* 0.53
 OTU-F5 (Bipolaris) 0.19±0.07 0.08±0.02* 0.43
 OTU-F6 (Bipolaris) 0.04±0 0.01±0.02* 0.25
 OTU-F7 (Bipolaris) 2.74±0.05 1.82±0.35** 0.66
 OTU-F8 (Bipolaris) 0.04±0.03 0±0*
 OTU-F9 (Bipolaris) 0.64±0.17 0.34±0.13* 0.52
 OTU-F10 (Bipolaris) 0.13±0.07 0.03±0.03* 0.20
 OTU-F11 (Bipolaris) 0.07±0.03 0.01±0.02** 0.13
 OTU-F12 (Bipolaris) 0.29±0.08 0.11±0.06* 0.36
 OTU-F13 (Bipolaris) 50.14±5.24 30.25±7.36** 0.60
 OTU-F14 (Bipolaris) 0.18±0.06 0.07±0.04* 0.40
 OTU-F15 (Bipolaris) 0.09±0.06 0.02±0.02* 0.20
 OTU-F16 (Bipolaris) 0.06±0.02 0.04±0* 0.57
 OTU-F17 (Bipolaris) 0.41±0.05 0.19±0.03*** 0.46
 OTU-F18 (Bipolaris) 0.04±0.03 0±0*
OTU-F19 (Podospora) 0±0 0.30±0.24*
OTU-F20 (Olpidium brassicae) 9.07±10.0 43.9±15.4** 4.84

a When the same or a similar value for relative abundance was obtained at different taxonomic levels for a fungal group, only the lowest taxonomic group was shown. Fungal groups showing a higher abundance in the CK plot than in the CO plot are shown in bold font.

b Relative abundance (%) is calculated based on 2,835 reads per sample and the results of the average and S.D. (n=4) for each of the fertilization conditions are shown.

c CO and CK indicate the compound fertilizer and Chiyoda-kasei plots, respectively.

d The closest taxon to the sequence of an OTU is shown in parentheses.

*, *, and *** indicate a significant difference between the CO and CK plots at P<0.05, P<0.01, and P<0.001, respectively.

Fig. 1.

Correlation plot of the relative abundance of Bipolaris and Olpidium. Panel A: Correlation plot at the genus level. Panel B: Correlation plot at the OTU level. *** indicates a significant difference at P<0.001.

The high dominance of Bipolaris sp. in the roots of napa cabbage cultivated in Japan may be attributed to Andosol. While Andosol is the most common soil type for upland crops in Japan, it has rarely been found in the countries in which previous studies conducted fungal community ana­lyses of the rhizospheres of Brassica species (Neupane et al., 2013; Lay et al., 2018; Picot et al., 2021). Bipolaris was shown to be relatively insensitive to volatile isothiocyanates (ITCs) originating from glucosinolates in the roots of Brassica species (Kirkegaard et al., 1996). Since Bipolaris is one of the most important fungal pathogens for plants (Bhunjun et al., 2020), further studies are warranted on this fungal group in relation to the soil type and fertilization practices. Furthermore, research involving culture-dependent methodologies is needed to reveal the ecological functionality of unknown Bipolaris.

As fungal groups that were significantly more abundant in the CK plot than in the CO plot, 2 taxa and 2 OTUs were identified (Table 3). Olpidium species are recognized as a common fungal parasite for the roots of diverse plant species, particularly in the family Brassicaceae (Hartwright et al., 2010), and the relative abundance of Olpidium (69.8%) in the roots of canola was previously reported to be high (Lay et al., 2018). Floc’h et al. (2020) showed that the low and high relative abundance of Olpidium positively and negatively correlated with the yields of canola and suggested the potential of a population dependent-change in the ecological role of Olpidium sp. Lebreton et al. (2019) hypothesized that for a non-mycorrhizal plant, an endophytic fungus, such as Opidium species, may play a role in plant nutrition uptake, similar to other crucifer plant-fungus interactions.

The relative abundance of Olpidium in the rhizospheres of oilseed rape and wheat was shown to increase under high nitrogen fertilization (Illescas et al., 2020; Picot et al., 2021). Since Olpidium is an obligate biotroph, it may be more susceptible to changes in the environmental conditions surrounding host plants than Bipolaris, which is generally considered to be a facultative fungal group. Lebreton et al. (2019) demonstrated that the relative abundance of an unknown Chytridiomycota markedly increased with a decrease in that of Ascomycota in the roots of napa cabbage in the later stage of vegetative growth. Therefore, the marked difference observed in relative abundance between Bipolaris (belonging to Ascomycota) and Olpidium (belonging to Chytridiomycota) in the present study may also reflect variations in the succession stages of root-associated fungal communities between the CO and CK plots towards the mature growth stage of the napa cabbage head.

Correlation ana­lyses were conducted between the growth parameters of napa cabbage and root-associated microbes listed in Tables 2 and 3 (Table 4 and Fig. S3). The results obtained revealed that ASV-B2 (Chitinophaga), ASV-B6 (Comamonadaceae), and Xylariaceae positively correlated with the growth parameters of napa cabbage. The closest relatives for ASV-B2 and ASV-B6 revealed by blast ana­lyses suggest that these bacterial ASVs exerted PGP effects. As microbial groups that negatively correlated with the growth parameters of napa cabbage, 3 taxa (Alphaproteobacteria, Caulobacteraceae, and Caulobacter) and 7 ASV or OTUs (ASV-B3 [Niastella] and 6 OTUs belonging to Bipolaris) were identified. It was reasonable that ASV-B3 (Niastella) negatively correlated with plant growth parameters because Niastella is considered to function as a denitrifier that may reduce the efficiency of fertilization.

Table 4. Relationships between plant growth parameters of napa cabbage and the relative abundance of napa cabbage root-associated microbes showing a significant difference between compound fertilizer and Chiyoda-kasei plots
Taxona Weight of all
above-ground tissueb
Head weight Ratio to head
weight
in above-ground
tissue
P, N R2 P, N R2 P, N R2
Bacteria
Alphaproteobacteria N 0.42 N 0.56* N 0.41
Caulobacteraceae N 0.43 N 0.57* N 0.46
Caulobacter N 0.54* N 0.77** N 0.68*
ASV-B2 (Chitinophaga) P 0.17 P 0.47 P 0.78**
 ASV-B3 (Niastella) N 0.52* N 0.59* N 0.45
ASV-B6 (Comamonadaceae) P 0.53* P 0.53* P 0.31
Fungi
Xylariaceae P 0.43 P 0.56* P 0.36
 OTU-F2 (Bipolaris) N 0.69* N 0.64* N 0.27
 OTU-F3 (Bipolaris) N 0.23 N 0.50* N 0.70**
 OTU-F4 (Bipolaris) N 0.19 N 0.42 N 0.61*
 OTU-F5 (Bipolaris) N 0.46 N 0.54* N 0.44
 OTU-F8 (Bipolaris) N 0.001 N 0.15 N 0.58*
 OTU-F15 (Bipolaris) N 0.50 N 0.59* N 0.50

a Microbial groups showing a significantly higher abundance in the CK plot (Chiyoda-kasei) than in the CO plot (a compound fertilizer) are shown in bold font.

b P, N, and R2 indicate a positive correlation, negative correlation, and decision coefficient, respectively.

* and ** indicate a significant difference at P<0.05 and P<0.01, respectively.

Correlations based on a confidence curve of the regression line at P<0.05 are highlighted in gray.

In conclusion, the present study suggests that qualitative differences among additional fertilizers most likely cause a shift in bacterial and fungal community structures in the napa cabbage root. The results obtained herein will facilitate our understanding of the effects of fertilization practices on plant-associated microbes and provide insights into the regulation of the plant-associated microbiome in an agronomic environment.

Citation

Ikeda, S., Okazaki, K., Tsurumaru, H., Suzuki, T., and Hirafuji, M. (2022) Effects of Different Types of Additional Fertilizers on Root-associated Microbes of Napa Cabbage Grown in an Andosol Field in Japan. Microbes Environ 37: ME22013.

https://doi.org/10.1264/jsme2.ME22013

Acknowledgements

A part of this study was supported by JST CREST Grant Number JPMJCR1512 and JSPS KAKENHI Grant Number 19K05759 from the Ministry of Education, Science, Sports and Culture of Japan.

References
 
© 2022 by Japanese Society of Microbial Ecology / Japanese Society of Soil Microbiology / Taiwan Society of Microbial Ecology / Japanese Society of Plant Microbe Interactions / Japanese Society for Extremophiles.
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