Effects of land‐use changes on soil organic nitrogen fractions in the black soil region of Northeast China

Abstract

AbstractSoil organic nitrogen (SON) accounts for more than 90% of the total nitrogen (TN) in black soil and is one of the most important indicators of soil fertility. However, the effect of land‐use changes on SON fractions is still unclear in black soil. Hence, natural grassland (uncultivated), farmland (converted from natural grassland), and artificial forestland (grain plots converted into forests) in the black soil region of Northeast China were selected for research. TN, available nitrogen (AN) and SON fractions (ammonia nitrogen (AMN), amino acid nitrogen (AAN), hydrolysable unknown nitrogen (HUN), acid insoluble nitrogen (AIN)) in the topsoil (0–20 cm), and subsoil (20–40 cm) were analysed and compared with elucidate the effects of land‐use changes on SON fractions. The results showed that compared with natural grasslands, the contents of TN and AN in farmlands were 49.1%–67.4% and 48.0%–67.7% less, respectively, and the content of AAN decreased the most in SON fractions, by 52.2%–76.7%, followed by the content of AMN, which decreased by 46.9%–70.7%. The contents of TN and AN in the artificial forestland increased by 18.8% and 30.6%, respectively, compared with those in the farmland. Other than AAN, the content of the SON fractions in the artificial forestland soils was greater than that of the farmland, and the content of HUN increased the most in the SON fractions, by 29.6%, followed by the content of AIN, which increased by 25.8%. The proportions of AMN and AAN in the TN of the natural grassland were 1.2 and 1.7 times those of the artificial forestland, respectively. In conclusion, after natural grassland is converted to farmland, it will destroy the original soil structure, change the physical and chemical properties of the soil, significantly reduce the soil nitrogen supply potential, and significantly decrease nitrogen accumulation. The conversion of grain plots into forestland significantly improved the soil nitrogen storage capacity, but the potential nitrogen supply did not reach the levels of the uncultivated lands. Changes in land use types lead to changes in soil structure and vegetation cover, which in turn alter soil nitrogen cycling. These results provide a scientific basis for evaluating the nitrogen supply capacity of different land‐use types. The study suggests that the land use structure in the area should be properly matched to restore soil nitrogen reservoirs and maintain and improve soil fertility, taking into account local environmental conditions.