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The fumigant 1,3-dichloropropene (1,3-D) is widely-used to control pathogenic bacteria, fungi, nematodes and insects in soil before a crop is planted. Although fumigants in general have been reported to have a ‘fertilizer effect’ in the soil by increasing nitrogen availability, little is known of how a specific fumigant such as 1,3-D affects available nitrogen. This study used real-time quantitative PCR (qPCR) and 16S rRNA gene amplicon sequencing techniques to investigate the effects of 1,3-D on microorganisms involved in nitrogen cycling that were present in 2 soils: Jiangxi lateritic red soil and Beijing fluvo-aquic soil. The fumigant 1,3-D temporarily decreased the abundance of 11 functional genes involved in nitrogen-fixing, nitrification and denitrification in both soil types. Different nitrogen cycling groups recovered to the unfumigated level in various incubation phases. Microorganisms containing nifH, nxrB, napA and qnorB genes were most vulnerable to 1,3-D fumigation. However, a stronger and longer inhibition effect of 1,3-D on these 11 functional genes was observed in Jiangxi soil than in Beijing soil. At the same time, the abundance of nifH, AOBamoA, nirS, qnorB and cnorB genes was significantly increased 59 days after 1,3-D fumigation. Fumigation with 1,3-D significantly reduced the nitrogen-fixing bacteria Azospirillum and Paenibacillus; the nitrifiers Nitrosomonas and Nitrospira; and the denitrifiers Pseudomonas, Paracoccus and Sphingomonas. Conversely, fumigation with 1,3-D increased the nitrogen-fixing bacteria Bradyrhizobium and Rhizobium; the nitrification bacteria Nitrosospira and Nitrolancea; and the denitrification bacteria Sphingobium, Alcanivorax, Bacillus, Streptomyces and Aeromonas. Fumigation with 1,3-D therefore caused significant shifts in the species composition and number of microbes directly involved in nitrogen cycling in the short-term. These results contribute toward a better understanding of the impact of 1,3-D fumigation on various types of soil nitrogen-cycling groups.

Dimethyl disulfide (DMDS), a soil fumigant, is an effective, broad-spectrum compound that often replaces bromomethane (MB) in the prevention and treatment of soil-borne diseases. However, the disadvantages of DMDS include toxicity, volatility, pungent odor, risk of human exposure, and environmental pollution. Cyclodextrin (CD) has been widely used as a carrier of chemicals in many industries due to its functional advantages and safety. In this study, a DMDS-controlled release formulation was developed by encapsulating DMDS in the cavity of 2-hydroxypropyl-β-cyclodextrin (HP-β-CD). This formulation reduced DMDS usage and production costs. Orthogonal experimental design, Fourier transform infrared (FT-IR), Scanning electron microscopy (SEM), Thermal gravity analysis (TGA) characterization, efficacy comparison, safety, and other aspects of the evaluation showed that under the best preparation conditions, the encapsulation rate was 81.49%. The efficacy of DMDS@HP-β-CD was similar to unformulated DMDS. The efficacy duration of the formulation was about two times longer than DMDS, and it was safer to use. This study reveals a cyclodextrin-DMDS formulation with reduced toxicity, longer duration, environmental safety and sustainability.

The transformation of phosphorus (P) compounds in soil depends largely on soil microbial communities and is sensitive to agricultural practices. However, the effects of soil fumigation on soil P, and microbes involved in P transformation, are unknown. Our results showed that chloropicrin (CP) fumigation significantly increased the available-P, Leached-P and active-P fractionation (inorganic P extracted from H2O, NaHCO3 and NaOH) in Shangdong and Miyun soils in the early stages of culture, while soil alkaline phosphatase (ALP) activity and phoD gene abundance decreased significantly. Leached-P in fumigated soil was positively correlated with increased active-P fractionation, indicating that it was an important source of soil Leached-P after fumigation. The changes in P-fractionation, Leached-P and ALP after fumigation were also significantly correlated with the composition of the microbial communities. CP fumigation briefly stimulated an increase in the abundance and diversity of phoD-harboring microbial communities and promoted the mineralization process of soil P. PICRUSt metagenomic analysis showed an increase in the relative abundance of microorganisms with involved in carbohydrate/lipid transport and metabolism functions after fumigation. These results suggest CP fumigation altered soil P transformation and phoD-harboring microbes that might lead to an increased risk of P enrichment in waterways.