Fertilization regimes affect crop yields through changes of diazotrophic community and gene abundance in soil aggregation.

Soil aggregates are extremely vulnerable to agricultural intensification and are important drivers of soil health, microbial diversity, and biogeochemical cycling. Despite its importance, there is a dearth of studies revealing how fertilization regimes influence diazotrophic community behind soil aggregates, as well as the potential consequences for crop yields. To do this, a two-decade fertilization of wheat-maize intercropping field experiment was conducted in Loess Plateau of China semiarid area under three treatments: no fertilizer, chemical and organic fertilizer. Moreover, we categorized soil aggregates as large macroaggregates (>2 mm), medium macroaggregates (1-2 mm), small macroaggregates (0.25-1 mm), microaggregates (< 0.25 mm) and rhizosphere soils aggregates. We found that soil aggregates exerted a much more influence on the nifH gene abundance than fertilization practices. Particularly, nifH gene abundance has been promoted with increasing the size of soil aggregates fraction without blank soil in the organic fertilization while its abundance presented contrast patterns in the chemical fertilization. Bipartite association networks indicated that different soil aggregates shaped niche differentiation of diazotrophic community behind fertilization regimes. Additionally, we found that organic fertilization strengthens the robustness of diazotrophic communities as well as increases the complexity of microbial networks by harboring keystone taxa. Mantel test results suggested that specific soil factors exerted more selective power on diazotrophic community and nifH gene abundance in the chemical fertilization. Furthermore, ß-diversity and nifH gene abundance of diazotrophic communities in the soil microaggregates jointly determine the crop yields. Collectively, our findings emphasize the key role of functional community diversity in sustaining soil cycling process and crop yields under long-term fertilization, and facilitate our understanding of the mechanisms underlying diazotrophic community in response to agricultural intensification, which could pave the way to sustainable agriculture through manipulating the functional taxa.

Soil pH determines arsenic-related functional gene and bacterial diversity in natural forests on the Taibai Mountain.

Arsenic-related functional genes are ubiquitous in microbes, and their distribution and abundance are influenced by edaphic factors. In arsenic-contaminated soils, soil arsenic content and pH determine the distribution of arsenic metabolizing microorganisms. In the uncontaminated natural ecosystems, however, it remains understudied for the key variable factor in determining the variation of bacterial assembly and mediating the arsenic biogeographical cycles. Here, we selected natural forest soils from southern and northern slopes along the altitudinal gradient of Taibai Mountain, China. The arsenic-related functional genes and soil bacterial community was examined using GeoChip 5.0 and high-throughput sequencing of 16S rRNA genes, respectively. It was found that arsenic-related functional genes were ubiquitous in tested forest soils. The gene arsB has the highest relative abundance, followed by arsC, aoxB, arrA, arsM, and arxA. The arsenic-related functional genes distribution on two slopes were decoupled from their corresponding bacterial community. Though there are higher abundance of bacterial communities on the northern slope than that on the southern slope, for arsenic-related functional genes, the abundance has the contrary trend which showing the more arsenic-related functional genes on the southern slope. In the top ten phyla, Proteobacteria and Actinobacteria were dominant phyla which affected the abundance of arsenic-related functional genes. Redundancy analysis and variance partitioning analysis indicated that soil pH, organic matter and altitude jointly determined the arsenic-related functional genes diversity in the two slopes of Taibai Mountain, and soil pH was a key factor. This indicates that the lower pH may shape more microbes with arsenic metabolic capacity. These findings suggested that soil pH plays a significant role in regulating the distribution of arsenic-related functional microorganisms, even for a forest ecosystem with an altitudinal gradient, and remind us the importance of pH in microbe mediated arsenic transformation.