Global cropland nitrous oxide emissions in fallow period are comparable to growing-season emissions

This study was supported by the Youth Innovation Program of Chinese Academy of Agricultural Sciences (No. Y2023QC02), the National Natural Science Foundation of China (42225102, 42301059, 32172129, 42207378), the National Key Research and Development Program of China (2021YFD1700801, 2022YFD2300400), Technology Research System-Green manure (Grant No. CARS-22-G-16).Peer reviewedPostprin

Nitrogen application rates need to be reduced for half of the rice paddy fields in China

This research was partially supported by the National Key Research and Development Program (2016YFD0800500), the Special Fund for Agro-scientific Research in the Public Interest (201003014, 201303089), National Natural Science Foundation of China (41773068) and the Newton Fund (Grant Ref: BB/N013484/1).Peer reviewedPostprin

Nitrogen loss through denitrification in soil under pasture in New Zealand : a thesis submitted in partial fulfilment of the requirements for the degree of Doctor of Philosophy in Soil Science at Massey University, Palmerston North, New Zealand

Denitrification is an important process in the N cycle that can affect the efficiency of use of soil nutrients and also the impact of agricultural activities on the wider environment. There have been few studies on the losses of N by denitrification from pasture soils. The current study was undertaken to investigate N loss through denitrification in a New Zealand pasture, and to examine relationships between denitrification and other environmental and soil factors. Denitrification was measured using the acetylene inhibition technique by incubating soil in a closed system. A study on the effect of storage concluded that a soil's moisture status and the duration of storage can affect the denitrification activity, as measured by a short-term assay. This effect can operate by changing both denitrification enzyme activities and the availability of substrate. Denitrification activities were greatest in the surface soil and generally decreased with depth in the soil profile. The decrease in denitrification activity with depth could be also attributed to both a decrease in enzyme activity and also decreasing availability of C and NO3-N. High coefficients of variation (CV) and skewed distributions of denitrification rate were always observed in the field. The log-normal distribution generally provided a better fit than the normal distribution for denitrification rates measured in the field. The variance in denitrification rate changed temporally, and depended on the soil moisture content and the grazing pattern. Amendment of soil cores with NO3-N and soluble-C, either singly or together, substantially decreased the skewness of the frequency distribution of denitrification rates. Denitrification rates varied according the location in the paddock. Highest rates were detected in the floor of a gully and in a gateway area. Denitrification rates followed a marked seasonal pattern, with higher rates being measured during the wet winter and lower rates during the dry summer. Higher denitrification rates were also observed during brief periods after rainfall events in the summer. An annual N loss of about 4.5 kg N ha-1 through denitrification was estimated in this dairy-farm paddock. Block grazing with cows at a high stocking rate increased the denitrification rate between 3 and 14 days after grazing under seasonally moist conditions. However, the total N loss through denitrification induced by grazing during that period was still very small, compared with the N returned by the grazing animals. Correlation and multiple regression analyses revealed that relationships between single core measurements of denitrification rates and other edaphic factors in the field were poor for the combined data set. However better relationships between denitrification rate and NO3-N concentration in the individual soil cores existed at high soil moisture contents, and better relationships between denitrification rate and respiration rate existed at low soil moisture contents. Mean denitrification rates from individual dates were positively correlated to soil moisture content. Regression equations derived from the mean-value data for each sampling date improved the prediction of the observed denitrification rate, compared to those from the individual data sets. Soil moisture content and NO3-N concentration accounted for 51% of the observed variability in denitrification rate in the field. Experiments conducted to obtain insights into factors regulating denitrification, by removing possible limitations to denitrification during the incubation, found that the addition of NO3-N solution to soil cores stimulated denitrification rates in all seasons. This result suggested that the NO3-N concentration, or more importantly, the accessibility of NO3-N to the denitrification sites in the pasture soil may have limited denitrification. Denitrification rates also increased when soluble-C was added to the soil cores, but the magnitude of the effect depended on other edaphic factors A separate study demonstrated that the presence of acetylene during the denitrification measurement also inhibited the nitrification process, and consequently could affect the NO3-N availability for denitrification in the soil. However, this study also indicated that inhibition of nitrification by acetylene did not affect short-term measurement of denitrification rate

Nitrogen Amendment Stimulated Decomposition of Maize Straw-Derived Biochar in a Sandy Loam Soil: A Short-Term Study.

This study examined the effect of nitrogen (N) on biochar stability in relation to soil microbial community as well as biochar labile components using δ13C stable isotope technology. A sandy loam soil under a long-term rotation of C3 crops was amended with biochar produced from maize (a C4 plant) straw in absence (BC0) and presence (BCN) of N and monitored for dynamics of carbon dioxide (CO2) flux, phospholipid fatty acids (PLFAs) profile and dissolved organic carbon (DOC) content. N amendment significantly increased the decomposition of biochar during the first 5 days of incubation (P < 0.05), and the proportions of decomposed biochar carbon (C) were 2.30% and 3.28% in BC0 and BCN treatments, respectively, during 30 days of incubation. The magnitude of decomposed biochar C was significantly (P < 0.05) higher than DOC in biochar (1.75%) and part of relatively recalcitrant biochar C was mineralized in both treatments. N amendment increased soil PLFAs concentration at the beginning of incubation, indicating that microorganisms were N-limited in test soil. Furthermore, N amendment significantly (P < 0.05) increased the proportion of gram-positive (G+) bacteria and decreased that of fungi, while no noticeable changes were observed for gram-negative (G-) bacteria and actinobacteria at the early stage of incubation. Our results indicated that N amendment promoted more efficiently the proliferation of G+ bacteria and accelerated the decomposition of relatively recalcitrant biochar C, which in turn reduced the stability of maize straw-derived biochar in test soil