Interacting effect of diclofop-methyl on the rice rhizosphere microbiome and denitrification
Graphical abstract
Introduction
The rhizosphere microbiome acts as a highly evolved external functional milieu for plants. Root microbiota plays critical role in plant growth [1,2], development (e.g. flowering time) [3], and pathogen resistance [4]. Plant-microbiota interactions in the rhizosphere also drive global biogeochemical cycles of N as they affect biological N utilization, as well as N loss [5,6] and anaerobic ammonium oxidation [6]. It has been shown that the community structure, abundance and function of root microbiota are affected by several biotic factors (plant phenotype and development stages) and abiotic factors (N limitation, anoxia, nanoparticles, pesticides) [[7], [8], [9], [10]]. Previous studies have shown that pesticides could also influence soil N cycling. For instance, Tenuta et al. found that the application of glyphosate in a grass sward increase the denitrification rate by 20- to 30-fold after a 14- and 49-d application compared to herbicide-untreated grass sward, which might result in greater nitrous oxide emission and N loss from soil [11]. It was also reported that diclofop-methyl (DM) decreased nitrification of urea nitrogen in soils [12]. Therefore, more studies in this area are critically needed in view of the importance of microbiota for plant growth and the potential negative side-effect of pesticides on the plant microbiome of target and non-target plants [13].
In Asian subtropical regions, Oryza sativa (rice) is one of the most important staple food and crop rotation is frequently used to increase the land utilization rate and improve soil fertility. Therefore, paddy soils used for farming other crops, e.g., soybean, oilseed rape and wheat and barley, which are heavily sprayed by DM, can in turn contaminate rice cultures [14]. DM, which is widely used to control graminaceous weeds, can inhibit acetyl-CoA carboxylase activity and decrease fatty acid synthesis in rice [14]. Moreover, residual DM in soil can affect a wide range of metabolic pathways and increase organic acid exudation in rice [[15], [16], [17]]. Since plant exudates (e.g., sugars, organic acids and amino acids) are the key drivers of the rhizosphere microbiome composition, the reported DM effect on root exudation raises the possibility that complex plant-microbiota interactions could modulate DM toxicity in rice as well as the abundance of specialized microorganisms affecting the biogeochemical cycles of nutrients and plant growth [18]. Although previous studies have shown that N cycling in soils could be affected by pesticide like glyphosate or DM [11,12], the interactions between rhizosphere microbiota, plant exudates and the presence of these pesticides remain largely enigmatic.
To better understand the interactions between soil N cycle and residual DM in rice cultures, we studied the effect of DM exposure on root exudation, rhizosphere microbiome and potential N loss in laboratory cultures of rice. The effect of DM on the rice rhizosphere and soil microbial community was examined using Illumina sequencing. The composition and concentrations of root exudates were also studied by GC–MS. Moreover, we evaluated the effects of DM exposure and soil microbial community on potential soil denitrification (and fertilizer loss) using qRT-PCR (transcription of a key denitrification-related gene) and 15N isotope-tracing by mass spectrometry.
Section snippets
DM exposure of rice cultures
Rice seeds (Oryza sativa L. japonica cv. Xiushui 63) were sterilized with 75% ethanol for 3 min and 0.1% HgCl for 15 min. The seeds were then thoroughly washed with sterile water. The sterile seeds were subsequently vernalized at 25 °C for 2 days. After 2 days, there was no obvious bacterial colony on the seeds, then the seeds were transferred onto plastics basketweave, which were soaked in 4 L of water, in a greenhouse. After 10 days, rice seedlings that were uniformly distributed were then
Profiling of root exudates in DM-exposed rice seedlings
Across all treatments, we identified 186 root exudates by GC–MS (data not shown). After the 5-d DM exposure, we found that the concentration of 28 root exudates was significantly different than that of the control. The 28 root exudates included 7 amino acids, 5 fatty acids, 7 sugars or sugars alcohol with the remaining dispersed in various molecule classes (hydrocarbon, amide, catechol, phthalate, nucleobase, hydroxy acid, carboxylic acid, hydroxy ketone, and terpene) (Table S1; Fig. 1A). Out
DM modulates root exudation as well as the richness of the rice rhizosphere microbiome
In response to several stressors, including pesticides, plants frequently increased root exudation, which in turn increase microbial biomass and richness in the rhizosphere [9,17,23,26]. Indeed, specific acidophilic bacteria species can be attracted by A. thaliania root exudates and gather around roots after exposure to trace imazethapyr concentrations [9]. Moreover, residual DM concentrations can also affect rice root metabolism and citrate exudation [14]. In the present study, we further show
Conclusions
The present study demonstrates that DM increases the diversity and richness of the rice rhizosphere microbiome, and, to a lesser extent, that of the non-rhizosphere microorganisms. Our results suggest that changes in the soil biosphere could be the result of increasing concentration of root exudates after DM exposure rather than direct effect of DM. Residual DM concentrations in rice cultures could potentially influence N cycling by affecting rice root microbiome community. The present study
Acknowledgments
This work was financially supported by National Key Research and Development Program of China (2017YFD0200503), and the National Natural Science Foundation of China.
(21577128, 21777144), CAS Pioneer Hundred Talents Program to H.F. Qian, and Xingjiang Uighur Autonomous Region Talent Project to H.F. Qian.
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