Biochar addition induced the same plant responses as elevated CO2 in mine spoil

Effects of biochar on soil microbial diversity and community structure in clay soil

Purpose

We determined the microbial community diversity and structure in soil samples under different amounts of biochar added. Meanwhile, we also researched the relationships between soil microbial and soil physicochemical properties.

Method

In this study, a field experiment was set up, with a total of three experimental treatments: no biochar application, 10 t/m3 biochar application, and 20 t/m3 application. High-throughput sequencing technologies were used for soil samples of different treatment groups to understand soil microbial diversity and community structure.

Results

We found that the soil physicochemical properties after biochar addition were better than those without biochar addition, and the alpha diversity was higher in biochar addition level of 20 t/m3 than other processing groups. Proteobacteria, Cyanobacteria, and Actinobacteria were the dominant phyla of this study. The dominant genera were Skermanella, Nostoc, Frankia, and Unclassified-p-protecbacteria. At the gate level, Actinobacteria had significant differences among the three groups with different addition amounts. The microbial community structure was mainly influenced by soil porosity, soil moisture content, nitrogen fertilizer, and potassium fertilizer other than soil phosphate fertilizer and organic matter.

Conclusions

The results suggested that changes under different amounts of biochar added generate changes in soil physicochemical properties and control the soil composition of microbial communities. This provides a new basis for soil improvement.

Soil-plant nitrogen isotope composition and nitrogen cycling after biochar applications

Biochar has strong potential to improve nitrogen (N) use efficiency in both agricultural and horticultural systems. Biochar is usually co-applied with full rates of fertiliser. However, the extent to which N cycling can be affected after biochar application to meet plant N requirement remains uncertain. This study aimed to explore N cycling up to 2 years after biochar application. We applied pine woodchip biochar at 0, 10 and 30 t ha^-1 (B0, B10, B30, respectively) in a macadamia orchard and evaluated the N isotope composition (δ¹⁵N) of soil, microbial biomass and macadamia leaves. Soil total N (TN) and inorganic N pools were also measured up to 2 years after biochar application. Biochar did not alter soil TN but soil NO₃^--N increased at months 12 and 24 after biochar application. Soil NO₃^--N concentrations were always over ideal levels of 15 μg g^-1 in B30 throughout the study. Stepwise regression indicated that foliar δ¹⁵N decreases after biochar application were explained by increased NO₃^--N concentrations in B30. Foliar TN and photosynthesis were not affected by biochar application. The soil in the high rate biochar plots had excess NO₃^--N concentrations (over 30 μg g^-1) from month 20 onwards. Therefore, N fertiliser applications could be adjusted to prevent excessive N inputs and increase farm profitability.

CO2 Elevation Accelerates Phenology and Alters Carbon/Nitrogen Metabolism vis-à-vis ROS Abundance in Bread Wheat

Wheat is an important staple food crop of the world and it accounts for 18-20% of human dietary protein. Recent reports suggest that CO₂ elevation (CE) reduces grain protein and micronutrient content. In our earlier study, it was found that the enhanced production of nitric oxide (NO) and the concomitant decrease in transcript abundance as well as activity of nitrate reductase (NR) and high affinity nitrate transporters (HATS) resulted in CE-mediated decrease in N metabolites in wheat seedlings. In the current study, two bread wheat genotypes Gluyas Early and B.T. Schomburgk differing in nitrate uptake and assimilation properties were evaluated for their response to CE. To understand the impact of low (LN), optimal (ON) and high (HN) nitrogen supply on plant growth, phenology, N and C metabolism, ROS and RNS signaling and yield, plants were evaluated under short term (hydroponics experiment) and long term (pot experiment) CE. CE improved growth, altered N assimilation, C/N ratio, N use efficiency (NUE) in B.T. Schomburgk. In general, CE decreased shoot N concentration and grain protein concentration in wheat irrespective of N supply. CE accelerated phenology and resulted in early flowering of both the wheat genotypes. Plants grown under CE showed higher levels of nitrosothiol and ROS, mainly under optimal and high nitrogen supply. Photorespiratory ammonia assimilating genes were down regulated by CE, whereas, expression of nitrate transporter/NPF genes were differentially regulated between genotypes by CE under different N availability. The response to CE was dependent on N supply as well as genotype. Hence, N fertilizer recommendation needs to be revised based on these variables for improving plant responses to N fertilization under a future CE scenario.

The effects of short term, long term and reapplication of biochar on soil bacteria

Biochar has been shown to affect soil microbial diversity and abundance. Soil microbes play a key role in soil nutrient cycling, but there is still a dearth of knowledge on the responses of soil microbes to biochar amendments, particularly for longer-term or repeated applications. We sampled soil from a field trial to determine the individual and combined effects of newly applied (1 year ago), re-applied (1 year ago into aged biochar) and aged (9 years ago) biochar amendments on soil bacterial communities, with the aim of identifying the potential underlying mechanisms or consequences of these effects. Soil bacterial diversity and community composition were analysed by sequencing of 16S rRNA using a Miseq platform. This investigation showed that biochar in soil after 1 year significantly increased bacterial diversity and the relative abundance of nitrifiers and bacteria consuming pyrogenic carbon (C). We also found that the reapplication of biochar had no significant effects on soil bacterial communities. Mantel correlation between bacterial diversity and soil chemical properties for four treatments showed that the changes in soil microbial community composition were well explained by soil pH, electrical conductivity (EC), extractable organic C and total extractable nitrogen (N). These results suggested that the effects of biochar amendment on soil bacterial communities were highly time-dependent. Our study highlighted the acclimation of soil bacteria on receiving repeated biochar amendment, leading to similar bacterial diversity and community structure among 9-years old applied biochar, repeated biochar treatments and control.