Graduate School of Agriculture, Hokkaido University, Kita 9 Nishi 9 Kita-Ku, Sapporo, Hokkaido 060-8589, Japan; Arid Land Research Center, Tottori University, 1390 Hamasaka, Tottori, Tottori 680-0001, Japan.
Research Faculty of Agriculture, Hokkaido University, Kita 9 Nishi 9 Kita-Ku, Sapporo, Hokkaido 060-8589, Japan.
Sci Total Environ. 2020 Oct 20;740:140006. doi: 10.1016/j.scitotenv.2020.140006. Epub 2020 Jun 6.
Nitrous oxide (NO) emissions from soils applied with livestock excreta have been widely reported previously. The highest NO emissions from soils are also often reported during thawing periods in cold regions where soil freezing is common. However, the combined effects of cow urine application and freeze-thaw events on NO emissions and the related enzyme activities are still not clear. Thus, we simulated a freeze-thaw event at -3 °C for 7 days, and then increased to 3 °C for 46 days using intact soil cores with cow urine (392 kg N ha). We compared the factors influencing the magnitudes of NO emissions through soil microbial processes with and without the freeze-thaw event. Dicyandiamide (DCD), an inhibitor of nitrification, was added to investigate the significance of nitrification on NO emissions. The NO emission rates from the urine-applied soils peaked to approximately 1000 μg NO-N m h immediately after the soils thawed. Soil freezing with urine application was significantly higher cumulative NO emissions (537 mg NO-N m), compared to non-frozen soils with urine (247 mg NO-N m) during the incubation period (54 days). The effect of DCD application on NO emissions was not clear during the freeze-thaw event, although nitrate production rates were reduced. After the freezing event, soil moisture (water-filled pore space) was significantly higher in the non-frozen soils compared to the frozen soils, due to a 9% decline in bulk density of frozen soils. Additionally, the impact of thawing on urease and denitrification enzyme activities was influenced by the urine application. Urine application increased the urease activity, while the freezing event decreased the magnitudes. The physical changes in the soils were also important controlling factors of the NO emissions from cow urine-applied soils in cold regions.
先前已有报道称,在施用牲畜粪便的土壤中会产生一氧化二氮(NO)排放。在寒冷地区,土壤经常冻结,解冻期的土壤中通常会产生最高的 NO 排放。然而,牛尿的应用和冻融事件对 NO 排放及相关酶活性的综合影响仍不清楚。因此,我们使用含有牛尿(392kgN/ha)的原状土芯模拟了为期 7 天的冻融事件,然后将温度升高至 3°C 并持续 46 天。我们比较了有和没有冻融事件时通过土壤微生物过程影响 NO 排放幅度的因素。双氰胺(DCD)是硝化抑制剂,添加它是为了研究硝化作用对 NO 排放的重要性。土壤解冻后,牛尿应用土壤中的 NO 排放速率迅速达到约 1000μgNO-N/m/h。与非冻结土壤相比,牛尿应用导致土壤冻结时的累积 NO 排放量(537mgNO-N/m)显著更高,在培养期(54 天)内。尽管硝酸盐生成速率降低,但在冻融事件期间,DCD 应用对 NO 排放的影响并不明显。在冻融事件后,由于冻结土壤的密度降低了 9%,非冻结土壤中的土壤水分(充满水的孔隙空间)明显高于冻结土壤。此外,解冻对脲酶和反硝化酶活性的影响也受到尿液应用的影响。牛尿的应用增加了脲酶活性,而冻结事件则降低了其活性。土壤的物理变化也是寒冷地区牛尿应用土壤中 NO 排放的重要控制因素。