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. 2023 Sep 14:14:1242469.
doi: 10.3389/fpls.2023.1242469. eCollection 2023.

Differential effects of cow dung and its biochar on Populus euphratica soil phosphorus effectiveness, bacterial community diversity and functional genes for phosphorus conversion

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Differential effects of cow dung and its biochar on Populus euphratica soil phosphorus effectiveness, bacterial community diversity and functional genes for phosphorus conversion

Yuxian Fan et al. Front Plant Sci. .

Abstract

Introduction: Continuous monoculture leading to soil nutrient depletion may cause a decline in plantation productivity. Cow dung is typically used as a cheap renewable resource to improve soil nutrient status. In this study, our purpose was to compare the effects of different cow dung return methods (direct return and carbonization return) on soil microbial communities and phosphorus availability in the root zone (rhizosphere soil and non-rhizosphere soil) of P.euphratica seedlings in forest gardens and to explore possible chemical and microbial mechanisms.

Methods: Field experiments were conducted. Two-year-old P.euphratica seedlings were planted in the soil together with 7.5 t hm-2 of cow dung and biochar made from the same amount of cow dung.

Results: Our findings indicated that the available phosphorus content in soil subjected to biochar treatment was considerably greater than that directly treated with cow dung, leading to an increase in the phosphorus level of both aboveground and underground components of P.euphratica seedlings. The content of Olsen-P in rhizosphere and non-rhizosphere soil increased by 134% and 110%, respectively.This was primarily a result of the direct and indirect impact of biochar on soil characteristics. Biochar increased the biodiversity of rhizosphere and non-rhizosphere soil bacteria compared with the direct return of cow dung. The Shannon diversity index of carbonized cow manure returning to field is 1.11 times and 1.10 times of that of direct cow manure returning to field and control, and the Chao1 diversity index is 1.20 times and 1.15 times of that of direct cow manure returning to field and control.Compared to the direct addition of cow dung, the addition of biochar increased the copy number of the phosphorus functional genes phoC and pqqc in the rhizosphere soil. In the biochar treatment, the abundance of the phosphate-solubilizing bacteria Sphingomonas and Lactobacillus was significantly higher than that in the other treatments, it is relative abundance was 4.83% and 2.62%, respectively, which indirectly improved soil phosphorus availability.

Discussion: The results indicated that different cow dung return methods may exert different effects on phosphorus availability in rhizosphere and non-rhizosphere soils via chemical and microbial pathways. These findings indicated that, compared to the direct return of cow dung, biochar return may exert a more significant impact on the availability of phosphorus in both rhizosphere and non-rhizosphere soils, as well as on the growth of P.euphratica seedlings and the microbial community.

Keywords: P effectiveness; P functional gene; cow dung biochar; microbial diversity; phosphate-solubilizing bacteria.

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Conflict of interest statement

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Figures

Figure 1
Figure 1
Effect of cow dung return and cow dung biochar return on Total P, Olsen-P, Al-P, Fe-P, O-P and MBP content of inter- and non-inter-rooted soils. Error bars indicate standard error of the mean (n=3). BC indicates cow dung biochar added; CD indicates cow dung added; NRS non-inter-rooted; RS inter-rooted. Different letters between treatments indicate significant differences (P < 0.05).
Figure 2
Figure 2
PCoA ranking of the structure of the inter-root and non-inter-root soil bacterial communities for different cow manure return methods and control treatments. BC indicates cow dung biochar added; CD indicates cow dung added; NRS non-inter-rooted; RS inter-rooted.
Figure 3
Figure 3
Stratified clustering and heat map of bacterial abundance in the first 25 OTUs of inter- and non-inter-rooted soil for different cattle manure return methods and control treatments. Each column in the heat map represents a sample and each row represents a taxonomic level. The colour scale indicates the abundance of genetic species, expressed as the standard deviation of the mean, with red indicating high abundance and blue indicating low abundance. BC indicates cow dung biochar added; CD indicates cow dung added; NRS non-inter-rooted; RS inter-rooted.
Figure 4
Figure 4
Comparison of the relative abundance (mean ± SE, n = 3) of inter- and non-inter-root soil phosphorus dissolving bacteria for different cow dung return methods and control treatments. BC indicates cow dung biochar added; CD indicates cow dung added; NRS non-inter-rooted; RS inter-rooted. Different letters between treatments indicate significant differences (P < 0.05).
Figure 5
Figure 5
Redundancy analysis (RDA) of inter- and non-inter-root soil bacteria and soil physicochemical properties for different cattle manure return methods and control treatments. CK indicates no addition; BC indicates addition of cow dung biochar; CD indicates addition of cow dung.
Figure 6
Figure 6
Quantitative analysis of phosphorus mineralization and solubilization genes in inter-root and non-root soils of different cow dung return methods and control treatments (copies g-1). Error bars indicate the standard error of the mean (n=3). BC indicates cow dung biochar added; CD indicates cow dung added; NRS non-inter-rooted; RS inter-rooted. Different letters between treatments indicate significant differences (P < 0.05).

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