1. 西北农林科技大学 资源环境学院/农业农村部西北旱地农业绿色低碳重点实验室, 陕西 杨凌,712100
2. 西北农林科技大学 水利与建筑工程学院, 陕西 杨凌,712100
3. 西北农林科技大学 中国旱区节水农业研究院, 陕西 杨凌,712100
4. 西北农林科技大学 水土保持研究所, 陕西 杨凌,712100
纸质出版:2023
移动端阅览
唐坤, 郑艺欣, 赵成政, 等. 不同水分条件下土壤N2O排放的动力学方程模拟[J]. 水土保持通报, 2023,43(6):106-114.
Tang Kun, Zheng Yixin, Zhao Chengzheng, et al. Simulation of Soil N2O Emissions Under Different Soil Moisture Conditions by Using Mixed Dynamic Equation[J]. Bulletin of Soiland Water Conservation, 2023, 43(6): 106-114.
唐坤, 郑艺欣, 赵成政, 等. 不同水分条件下土壤N2O排放的动力学方程模拟[J]. 水土保持通报, 2023,43(6):106-114. DOI: 10.13961/j.cnki.stbctb.2023.06.014.
Tang Kun, Zheng Yixin, Zhao Chengzheng, et al. Simulation of Soil N2O Emissions Under Different Soil Moisture Conditions by Using Mixed Dynamic Equation[J]. Bulletin of Soiland Water Conservation, 2023, 43(6): 106-114. DOI: 10.13961/j.cnki.stbctb.2023.06.014.
[目的
]
水分对土壤N
2
O排放有重要影响。运用混合动力学方程模拟不同水分条件下土壤N
2
O累积排放的过程,分析土壤水分对N
2
O产生途径的影响及其变化规律,为通过改善土壤管理降低N
2
O气体排放提供理论和实践指导。[方法
]
通过室内培养试验,研究了不同水分条件〔40% WHC,60% WHC,80% WHC,100% WHC和淹水处理,WHC(田间持水量)〕下土壤N
2
O排放特征、硝铵态氮含量和氧气消耗动态变化。[结果
]
①N
2
O排放速率24 h时达到最大,淹水处理〔3.46 μg/(kg·h)〕是其他处理的54.5~178.9倍。②土壤N
2
O累积排放量均随着培养时间的延长而增加,淹水处理的快速上升阶段为前48 h,而其他处理为前96 h。培养结束时的土壤N
2
O累积排放量,淹水处理(44.6 μg/kg)分别是40% WHC,60% WHC,80% WHC和100% WHC的67.1,29.2,20.8,10.4倍。③除淹水条件下,伪二级动力学方程的决定系数(R
2
)为0.878以外,其余均在0.92以上。培养初期24 h时,反硝化过程的N
2
O排放所占比例9.3%~13.2%,硝化过程为86.8%~90.7%;培养结束480 h时,反硝化过程的N
2
O排放所占比例为37.8%~47.5%,硝化过程为52.5%~62.2%。[结论
]
土壤水分含量越高N
2
O的排放量越大,并且在24 h出现排放速率脉冲。淹水条件下N
2
O主要由反硝化过程产生,而40% WHC~100% WHC条件下主要由硝化过程产生。混合动力学方程可以很好地模拟培养过程中土壤N
2
O的累积排放过程,并且可以用来区分反硝化和硝化过程的N
2
O排放量和所占比例。这为研究土壤N
2
O产生和排放途径提供了一种新的思路和方法,结果还有待通过田间试验以及同位素示踪方法等进一步验证。
[Objective] Soil moisture has an important impact on N2O emissions. This study attempted to simulate the cumulative process of soil N2O emission under different soil moisture conditions by using a mixed dynamic equation
and to analyze the influence of soil water on N2O production pathway and its variation rule in order to provide theoretical and practical guidance for reducing N2O gas emissions through improving soil management. [Methods] Soil N2O emission characteristics
the dynamics of ammonium and nitrate nitrogen content
and oxygen consumption were studied under different soil moisture conditions [40% water-holding capacity (WHC)
60% WHC
80% WHC
100% WHC
and flooded]. [Results] ① The N2O emission rates reached maximum values at 24 h. Emissions from the flooded treatment [3.46 μg/(kg·h)] were 54.5-178.9 times greater than from the other treatments. ② The cumulative emission of soil N2O increased with increasing incubation time
and the rapid rise stage occurred in the first 48 h for the flooded treatment. The rapid rise stage occurred in the first 96 h for other treatments. The cumulative N2O emissions for soil under the flooded treatment (44.6 μg/kg) were 67.1
29.2
20.8
and 10.4 times greater than under 40% WHC
60% WHC
80% WHC and 100% WHC
respectively
at the end of incubation. ③ Except for the coefficient of determination (R2) of 0.878 for the pseudo-second-order dynamic equation under the flooded treatment
all coefficients of determination were greater than 0.920 for all dynamic equations under all soil moisture treatments. The denitrification process accounted for 9.3%~13.2% of the N2O emissions
and the nitrification process accounted for 86.8%~90.7% of the N2O emissions at the initial 24 h of incubation. At the end of incubation (480 h)
the denitrification process accounted for 37.8%~47.5% of the N2O emissions
and the nitrification process accounted for 52.5%~62.2% of the N2O emissions. [Conclusion] The higher the soil moisture content
the greater the emission of N2O
and an emission rate pulse appeared at 24 h. N2O was mainly generated by denitrification under flooded conditions. N2O was mainly generated by nitrification under the 40%~100% WHC conditions. The mixed dynamic equation was able to well simulate the cumulative emission process of soil N2O during the incubation experiment
and can be used to distinguish the amount and proportion of N2O emissions occurring by denitrification and nitrification processes. These results provide a new idea and method for studying the pathways of soil N2O production and emission. The results need to be further verified by field experiments and isotope tracing methods etc.
Müller R.The impact of the rise in atmospheric nitrous oxide on stratospheric ozone [J].Ambio, 2021,50(1):35-39.
Kroeze C, Mosier A, Bouwman L.Closing the global N
2
O budget:a retrospective analysis 1500-1994[J].Global Biogeochemical Cycles, 1999,13(1):1-8.
Goldberg S D, Gebauer G.Drought turns a Central European Norway spruce forest soil from an N
2
O source to a transient N
2
O sink [J].Global Change Biology, 2009,15(4):850-860.
Cui Feng, Yan Guangxuan, Zhou Zaixing, et al.Annual emissions of nitrous oxide and nitric oxide from a wheat-maize cropping system on a silt loam calcareous soil in the North China Plain [J].Soil Biology and Biochemistry, 2012,48:10-19.
曹文超,宋贺,王娅静,等.农田土壤N
2
O排放的关键过程及影响因素[J].植物营养与肥料学报,2019,25(10):1781-1798.
Bracken C J, Lanigan G J, Richards K G, et al.Sward composition and soil moisture conditions affect nitrous oxide emissions and soil nitrogen dynamics following urea-nitrogen application [J].Science of the Total Environment, 2020,722:137780.
郑欠,丁军军,李玉中,等.土壤含水量对硝化和反硝化过程N
2
O排放及同位素特征值的影响[J].中国农业科学,2017,50(24):4747-4758.
唐瑞杰,胡煜杰,赵彩悦,等.不同水分条件下土地利用方式对我国热带地区土壤硝化过程及NO和N
2
O排放的影响[J].环境科学,2022,43(11):5159-5168.
Szukics U, Abell G C J, Hodl V, et al.Nitrifiers and denitrifiers respond rapidly to changed moisture and increasing temperature in a pristine forest soil [J].Fems Microbiology Ecology, 2010,72(3):395-406.
李平,魏玮,郎漫.不同水分对半干旱地区砂壤土温室气体排放的短期影响[J].农业环境科学学报,2021,40(5):1124-1132.
Wu Di, Cárdenas L M, Calvet S, et al.The effect of nitrification inhibitor on N
2
O, NO and N
2
emissions under different soil moisture levels in a permanent grassland soil [J].Soil Biology and Biochemistry, 2017,113:153-160.
Zhou Junyu, Gu Baojing, Schlesinger W H, et al.Significant accumulation of nitrate in Chinese semi-humid croplands [J].Scientific Reports, 2016,6:25088.
Havlin L J, Westfall G D.Potassium release kinetics and plant response in calcareous soils [J].Soil Science Society of America Journal, 1985,49(2):366-370.
薛泉宏,尉庆丰,高彦,等.陕西省几种代表性土壤NH
4
+
吸附、解吸动力学特征研究[J].土壤学报,1996,33(2):129-137.
乔玮,毕少杰,尹冬敏,等.鸡粪中高温厌氧甲烷发酵产气潜能与动力学特性[J].中国环境科学,2018,38(1):234-243.
Li Huilin, Han Yong, Cai Zucong.Nitrogen mineralization in paddy soils of the Taihu Region of China under anaerobic conditions:Dynamics and model fitting [J].Geoderma, 2003,115(3/4):161-175.
Benbi D K, Richter J.A critical review of some approaches to modelling nitrogen mineralization [J].Biology and Fertility of Soils, 2002,35(3):168-183.
Bonde T A, Rosswall T.Seasonal variation of potentially mineralizable nitrogen in four cropping systems [J].Soil Science Society of America Journal, 1987,51(6):1508-1514.
Heumann S, Böttcher J, Springob G.N mineralization parameters of sandy arable soils [J].Journal of Plant Nutrition and Soil Science, 2002,165(4):441-450.
牛金璨,张丽娜,张亚美,等.钾钠离子添加对土壤团聚体和有机碳矿化的影响[J].植物营养与肥料学报,2022,28(5):786-797.
苏王娟,李勇,石辉,等.温度和水分对长沙市丘陵马尾松林红壤N
2
O排放的影响:一个室内培养试验[J].林业科学,2013,49(3):152-158.
鲍士旦.土壤农化分析[M].3版.北京:中国农业出版社,2000.
王连峰,蔡祖聪.水分和温度对旱地红壤硝化活力和反硝化活力的影响[J].土壤,2004,36(5):543-546,560.
Highton M P, Bakken L R, Dörsch P, et al.Soil N
2
O emission potential falls along a denitrification phenotype gradient linked to differences in microbiome, rainfall and carbon availability [J].Soil Biology and Biochemistry, 2020,150:108004.
Bonetti G, Limpert K E, Brodersen K E, et al.The combined effect of short-term hydrological and N-fertilization manipulation of wetlands on CO
2
, CH
4
, and N
2
O emissions [J].Environmental Pollution, 2022,294:118637.
Liu Yu, Cong Rihuan, Liao Shipeng, et al.Rapid soil rewetting promotes limited N
2
O emissions and suppresses NH
3
volatilization under urea addition [J].Environmental Research, 2022,212:113402.
刘俊民,郭瑞.关中平原降水特征分析[J].人民黄河,2008,30(5):22-24.
蔡新玲,叶殿秀,孙娴,等.1961-2011年陕西省汛期短时降水变化特征[J].高原气象,2014,33(6):1618-1626.
Lang Man, Cai Zucong, Mary B, et al.Land-use type and temperature affect gross nitrogen transformation rates in Chinese and Canadian soils [J].Plant and Soil, 2010,334:377-389.
夏品华,喻理飞,曹海鹏,等.贵州草海人工湿地系统硝化-反硝化作用研究[J].生态环境学报,2015,24(12):2045-2049.
Stevens R J, Laughlin R J, Burns L C, et al.Measuring the contributions of nitrification and denitrification to the flux of nitrous oxide from soil [J].Soil Biology and Biochemistry, 1997,29(2):139-151.
Zhu Xia, Burger M, Doane T A, et al.Ammonia oxidation pathways and nitrifier denitrification are significant sources of N
2
O and NO under low oxygen availability [J].Proceedings of the National Academy of Sciences of the United States of America, 2013,110(16):6328-6333.
Kool D M, Dolfing J, Wrage N, et al.Nitrifier denitrification as a distinct and significant source of nitrous oxide from soil [J].Soil Biology and Biochemistry, 2011,43(1):174-178.
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