Scientia Agricultura Sinica ›› 2020, Vol. 53 ›› Issue (13): 2614-2624.doi: 10.3864/j.issn.0578-1752.2020.13.010

• TECHNOLOGY AND MECHANISM OF TEMPERATE MEADOW STEPPE RESTORATION • Previous Articles     Next Articles

Effects of Organic Fertilizer on Soil Bacterial Community Diversity in Leymus chinensis Steppe

SHANG LiRong,WAN LiQiang(),LI XiangLin()   

  1. Institute of Animal Sciences, Chinese Academy of Agricultural Sciences, Beijing 100193
  • Received:2019-08-12 Accepted:2019-12-25 Online:2020-07-01 Published:2020-07-16
  • Contact: LiQiang WAN,XiangLin LI E-mail:wanliqiang@caas.cn;lxl@caas.cn

Abstract:

【Objective】 In order to provide a practical and scientific basis for improvement, restoration and reasonable use of degraded grassland, the effects of different organic fertilizers on soil nutrient status and soil bacterial diversity were revealed in the natural Leymus chinensis steppe degraded grassland in Hulunbeier. 【Method】 The field experiments were designed by single factor randomized block design, and the seven treatments were as follows: the control (ck), vermicompost 15 t·hm-2(a1), 30 t·hm-2(a2), 45 t·hm-2(a3), mushroom residues 15 t·hm-2(b1), 30 t·hm-2(b2), 45 t·hm-2(b3). Combined with the physical and chemical properties of soil, this study used the high-throughput sequencing technology of Miseq to analyze the effects of different organic fertilizer treatments on the diversity of soil bacterial communities, and to explore the environmental drivers of bacterial community changes under different organic fertilizer treatments. 【Result】 The results showed that organic fertilization improved the soil nutrient status and shaped the distinct bacterial communities. Compared with ck, the AP content increased significantly by 37.27% under a3 treatment. AK content under b3 and a3 treatments increased significantly by 62.99% and 40.53% compared with the control, respectively. And aboveground biomass was significantly higher than other treatments under b3 treatment (244.11 g·m-2). Moreover, vermincompost and mushroom residues fertilizers significantly increased the richness of the bacterial community. Compared with ck, the richness index increased significantly under a1 and b2 treatments. At the phylum level, a total of 31 taxa were obtained from 21 samples. Actinobacteria, Proteobacteria, Acidobacteria, Verrucomicrobia and Chloroflexi were the dominant groups, and relative abundances account for the bacterial community 85% or more. Actinomycetes were the most abundant under a2 treatment (36.79%). Proteobacteria was higher under b1 and b3 treatments (23.29% and 22.32%, resptectively). Acidobacteria was the highest under a1 treatment (20.69%). And LEfSe showed that more bacterial taxonomic groups were detected under b3 treatment (17 clades, 1 class, 1 order, 4 families and 11 genera). In addition, AN (P=0.001), AK (P=0.005), and SOM (P=0.006) had extremely significant effects on the composition of bacterial communities in the soil (P<0.01), while TK (P=0.014) had not. The composition of soil bacterial community had a significant effect (P<0.05). It showed that AN, AK, SOM and TK were the main driving factors of bacterial community. 【Conclusion】 Organic fertilizer changed the soil bacterial community structure in Leymus chinensis steppe. Our results indicated vermicompost and mushroom residues at 45 t·hm-2 increased available nutrient content, but also enhanced the biodiversity of soil bacterial communities in the grasslands of Leymus chinensis, which contributed to the sustainable development of grassland agro-ecosystems.

Key words: organic fertilizer, soil nutrient, soil bacterial community, Leymus chinensis steppe

Table 1

Chemical properties and aboveground biomass of the soils in different organic fertilization treatments"

处理
Treatment
pH 全氮
TN (g·kg-1)
全磷
TP (g·kg-1)
全钾
TK (g·kg-1)
有效氮
AN (mg·kg-1)
有效磷
AP (mg·kg-1)
有效钾
AK (mg·kg-1)
有机质
SOM (g·kg-1)
生物量
DM (g·m-2)
ck 6.28±0.10b 2.51±0.25a 0.66±0.12a 31.85±0.61a 172.84±10.24a 7.43±0.94b 179.42±31.01c 55.48±0.90a 172.8±10.68c
a1 6.31±0.02b 2.52±0.30a 0.68±0.10a 32.64±1.44a 175.90±11.67a 8.89±1.39b 209.19±55.79bc 52.15±6.19a 198.38±14.94bc
a2 6.51±0.11b 2.26±0.12a 0.69±0.21a 31.96±0.84a 167.76±3.12a 8.34±1.29b 195.03±32.10bc 50.32±5.18a 180.91±2.90bc
a3 7.02±0.54a 2.47±0.08a 0.73±0.20a 33.12±0.71a 184.54±15.22a 10.20±0.15a 252.14±4.68ab 55.40±5.49a 214.27±5.26bc
b1 6.21±0.08b 2.56±0.28a 0.74±0.26a 32.18±0.51a 183.70±3.66a 9.06±1.87b 250.67±12.13ab 55.75±1.76a 191.49±1.99ab
b2 6.14±0.12b 2.10±0.07a 0.58±0.04a 31.84±0.56a 169.34±6.80a 8.18±0.48b 220.20±23.32bc 48.31±5.60a 219.78±10.73ab
b3 6.17±0.20b 2.40±0.26a 0.55±0.01a 32.59±0.88a 187.96±5.60a 8.84±0.31b 292.44±20.67a 55.78±4.43a 244.11±13.59a

Table 2

Illumina MiSeq sequencing results and α-diversity of the bacterial community with different organic fertilizer treatments"

处理
Treatment
序列数
Reads
操作分类单元
Observed OTU
香农指数
Shannon index
Ace指数
Ace index
覆盖度
Coverage
ck 35708 2272.67±52.80b 6.43±0.06a 2703.45±53.03b 0.9849±0.0002a
a1 35708 2411.00±15.80ab 6.53±0.01a 2894.58±19.41a 0.9837±0.0002a
a2 35708 2396.00±39.38ab 6.47±0.03a 2848.59±58.42ab 0.9841±0.0009a
a3 35708 2301.67±18.31ab 6.39±0.02a 2755.35±23.34ab 0.9843±0.0003a
b1 35708 2303.67±72.76ab 6.38±0.07a 2791.93±88.16ab 0.9838±0.0009a
b2 35708 2436.00±1.70a 6.51±0.02a 2898.92±18.63a 0.9838±0.0004a
b3 35708 2372.00±54.95ab 6.45±0.06a 2839.53±76.17ab 0.9839±0.0011a

Fig. 1

Structures of bacterial community composition at the phylum levels under different organic fertilization treatments"

Fig. 2

PLS-DA diagram of soil bacterial community with different organic fertilizers treatment"

Fig. 3

The cladogram of soil bacterial community under different organic fertilizer treatments"

Fig. 4

Canonical correspondence analysis (RDA) based on the relative abundance of bacterial at genus level and selected soil chemical properties among different organic fertilization treatments"

Table 3

P value based on the correlation between bacterial communities and environmental factors at the genus level (n=3)"

环境因子Environmental factor r P
全氮TN 0.1248 0.315
全磷TP 0.2754 0.050
全钾TK 0.4301 0.017
有效氮AN 0.6618 0.001
有效磷AP 0.2268 0.108
有效钾AK 0.5749 0.004
有机质SOM 0.5893 0.004
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