Please wait a minute...
Journal of Integrative Agriculture  2023, Vol. 22 Issue (1): 251-264    DOI: 10.1016/j.jia.2022.08.009
Agro-ecosystem & Environment Advanced Online Publication | Current Issue | Archive | Adv Search |
Reduction of N2O emissions by DMPP depends on interaction of nitrogen source (digestate vs. urea) with soil properties
LI Hao-ruo1, SONG Xiao-tong2Lars R. BAKKEN4, JU Xiao-tang1, 3

1 College of Resources and Environmental Sciences, China Agricultural University, Beijing 100193, P.R.China

2 State Key Laboratory of Urban and Regional Ecology, Research Center for Eco-Environmental Sciences, Chinese Academy of Sciences, Beijing 100085, P.R.China

3 College of Tropical Crops, Hainan University, Haikou 570228, P.R.China

4 Faculty of Chemistry, Biotechnology and Food Science, Norwegian University of Life Science (NMBU), Ås 1430, Norway 

Download:  PDF in ScienceDirect  
Export:  BibTeX | EndNote (RIS)      
摘要  

通过硝化抑制剂(NI)与肥料混合施用来抑制硝化作用,是一种降低肥料导致氧化亚氮(N2O)排放有效方法3,4-二甲基吡唑磷酸盐(DMPP)对氨氧化细菌(AOB)的抑制效果明显大于氨氧化古菌(AOA),AOBAOA分别在碱性和酸性土壤中主导硝化作用。然而,氮源与土壤性质的相互作用对DMPP 功效的影响仍不清楚。因此,我们通过施加不同浓度DMPP,选用digestate和尿素作为肥料,对三种pH不同的中国典型农田土壤潮土、黑土和红土)进行了微宇宙试验。在碱性潮土中,施用尿素和digestate均引发N2O排放高峰(60 ug N kg-1 day-1),与施肥后3天内快速的硝化作用相一致DMPP减少约90% N2O排放,尽管硝化速率仅降低50%。在酸性黑土中,只有digestate促进N2O排放,其排放量随时间逐渐增加,在5-7天后出现排放高峰20 ug N kg-1 day-1)。在黑土中,DMPP对硝化速率和N2O排放均有轻微的抑制,N2O产率(N2O-N/NO2-+NO3--N )高达3.5%,表明digestate诱导了异养反硝化作用。在酸性红壤中,digestate和尿素处理的N2O排放峰值分别为5010 ug N kg-1 day-1DMPP使该速率大幅下降70%。与0.5% DMPP处理相比,更高浓度的DMPP1.0-1.5%这些土壤中包括digestate和尿素)对N2O排放的抑制作用均不显著P<0.05)。我们的研究强调了氮源、土壤性质和NI的匹配对高效减少N2O排放的重要性



Abstract  


The inhibition of nitrification by mixing nitrification inhibitors (NI) with fertilizers is emerging as an effective method to reduce fertilizer-induced nitrous oxide (N2O) emissions.  The additive 3,4-dimethylpyrazole phosphate (DMPP) apparently inhibits ammonia oxidizing bacteria (AOB) more than ammonia oxidizing archaea (AOA), which dominate the nitrification in alkaline and acid soil, respectively.  However, the efficacy of DMPP in terms of nitrogen sources interacting with soil properties remains unclear.  We therefore conducted a microcosm experiment using three typical Chinese agricultural soils with contrasting pH values (fluvo-aquic soil, black soil and red soil), which were fertilized with either digestate or urea in conjunction with a range of DMPP concentrations.  In the alkaline fluvo-aquic soil, fertilization with either urea or digestate induced a peak in N2O emission (60 μg N kg–1 d–1) coinciding with the rapid nitrification within 3 d following fertilization.  DMPP almost eliminated this peak in N2O emission, reducing it by nearly 90%, despite the fact that the nitrification rate was only reduced by 50%.  In the acid black soil, only the digestate induced an N2O emission that increased gradually, reaching its maximum (20 μg N kg–1 d–1) after 5–7 d.  The nitrification rate and N2O emission were both marginally reduced by DMPP in the black soil, and the N2O yield (N2O-N per NO2+NO3-N produced) was exceptionally high at 3.5%, suggesting that the digestate induced heterotrophic denitrification.  In the acid red soil, the N2O emission spiked in the digestate and urea treatments at 50 and 10 μg N kg–1 d–1, respectively, and DMPP reduced the rates substantially by nearly 70%.  Compared with 0.5% DMPP, the higher concentrations of DMPP (1.0 to 1.5%) did not exert a significantly (P<0.05) better inhibition effect on the N2O emissions in these soils (either with digestate or urea).  This study highlights the importance of matching the nitrogen sources, soil properties and NIs to achieve a high efficiency of N2O emission reduction.


Keywords:  nitrous oxide       digestate       urea       nitrification inhibitors       DMPP       alkaline soils       acid soils  
Received: 10 December 2021   Accepted: 24 January 2022
Fund: 

This work was financially supported by the National Natural Science Foundation of China (31861133018, 41830751, and 42107320) and the Hainan University Startup Fund, China (KYQD(ZR)-20098).  We sincerely thank Prof. Zhang Xiaojun in Shanghai Jiao Tong University, China for providing the digestate.


About author:  LI Hao-ruo, E-mail: lihaoruo1995@163.com; Correspondence SONG Xiao-tong, E-mail: xtsong@rcees.ac.cn; JU Xiao-tang, E-mail: juxt@cau.edu.cn

Cite this article: 

LI Hao-ruo, SONG Xiao-tong, Lars R. BAKKEN, JU Xiao-tang. 2023. Reduction of N2O emissions by DMPP depends on interaction of nitrogen source (digestate vs. urea) with soil properties. Journal of Integrative Agriculture, 22(1): 251-264.

Chantigny M H, Angers D A, Rochette P, Belanger G, Masse D, Cote D. 2007. Gaseous nitrogen emissions and forage nitrogen uptake on soils fertilized with raw and treated swine manure. Journal of Environmental Quality, 36, 1864–1872. 
Collins H P, Alva A K, Streubel J D, Fransen S F, Frear C, Chen S, Kruger C, Granatstein D. 2011. Greenhouse gas emissions from an irrigated silt loam soil amended with anaerobically digested dairy manure. Soil Science Society of America Journal, 75, 2206–2216. 
Comfort S, Kelling K, Keeney D, Converse J. 1990. Nitrous oxide production from injected liquid dairy manure. Soil Science Society of America Journal, 54, 421–427. 
Cui P, Fan F, Yin C, Song A, Huang P, Tang Y, Zhu P, Peng C, Li T, Wakelin S A, Liang Y. 2016. Long-term organic and inorganic fertilization alters temperature sensitivity of potential N2O emissions and associated microbes. Soil Biology and Biochemistry, 93, 131–141.
Di H J, Cameron K C. 2011. Inhibition of ammonium oxidation by a liquid formulation of 3,4-dimethylpyrazole phosphate (DMPP) compared with a dicyandiamide (DCD) solution in six New Zealand grazed grassland soils. Journal of Soils and Sediments, 11, 1032–1039. 
Dong D, Yang W, Sun H, Kong S, Xu H. 2021. Nitrous oxide emissions in response to long-term application of the nitrification inhibitor DMPP in an acidic luvisol. Applied Soil Ecology, 159, 103861. 
Dong X X, Zhang L L, Wu Z J, Li D P, Gong P. 2013. Effects of the nitrification inhibitor DMPP on soil bacterial community in a Cambisol in Northeast China. Journal of Soil Science and Plant Nutrition, 13, 580–591.
Duan P, Shen H, Jiang X, Yan X, Xiong Z. 2020. The contributions of hydroxylamine and nitrite to NO and N2O production in alkaline and acidic vegetable soils. Journal of Soils and Sediments, 20, 2903–2911. 
Duan Y F, Kong X W, Schramm A, Labouriau R, Eriksen J, Petersen S O. 2017. Microbial N transformations and N2O emission after simulated grassland cultivation: Effects of the nitrification inhibitor 3,4-dimethylpyrazole phosphate (DMPP). Applied and Environmental Microbiology, 83, e02019–e02035.
Fan X, Yin C, Chen H, Ye M, Zhao Y, Li T, Wakelin S A, Liang Y. 2019. The efficacy of 3,4-dimethylpyrazole phosphate on N2O emissions is linked to niche differentiation of ammonia oxidizing archaea and bacteria across four arable soils. Soil Biology and Biochemistry, 130, 82–93. 
FAO (Food and Agriculture Organization). 1988. FAO/Unesco soil map of the world. Revised legend with corrections. In: World Resources Report 60. FAO, Rome. 
Florio A, Clark I M, Hirsch P R, Jhurreea D, Benedetti A. 2014. Effects of the nitrification inhibitor 3,4-dimethylpyrazole phosphate (DMPP) on abundance and activity of ammonia oxidizers in soil. Biology and Fertility of Soils, 50, 795–807. 
Florio A, Maienza A, Dell’Abate M T, Stazi S R, Benedetti A. 2016. Changes in the activity and abundance of the soil microbial community in response to the nitrification inhibitor 3,4-dimethylpyrazole phosphate (DMPP). Journal of Soils and Sediments, 16, 2687–2697. 
Friedl J, Scheer C, Rowlings D W, Mumford M T, Grace P R. 2017. The nitrification inhibitor DMPP (3,4-dimethylpyrazole phosphate) reduces N2 emissions from intensively managed pastures in subtropical Australia. Soil Biology and Biochemistry, 108, 55–64.
Guardia G, Marsden K A, Vallejo A, Jones D L, Chadwick D R. 2018. Determining the influence of environmental and edaphic factors on the fate of the nitrification inhibitors DCD and DMPP in soil. Science of the Total Environment, 624, 1202–1212. 
Hatch D, Trindade H, Cardenas L, Carneiro J, Hawkins J, Scholefield D, Chadwick D. 2005. Laboratory study of the effects of two nitrification inhibitors on greenhouse gas emissions from a slurry-treated arable soil: impact of diurnal temperature cycle. Biology and Fertility of Soils, 41, 225–232. 
He T, Yuan J, Luo J, Wang W, Fan J, Liu D, Ding W. 2019. Organic fertilizers have divergent effects on soil N2O emissions. Biology and Fertility of Soils, 55, 685–699.
Hink L, Nicol G W, Prosser J I. 2017. Archaea produce lower yields of N2O than bacteria during aerobic ammonia oxidation in soil. Environmental Microbiology, 19, 4829–4837. 
Huang T, Yang H, Huang C, Ju X. 2017. Effect of fertilizer N rates and straw management on yield-scaled nitrous oxide emissions in a maize–wheat double cropping system. Field Crops Research, 204, 1–11. 
ten Huf M, Olfs H W. 2020. Effect of the nitrification inhibitor DMPP on nitrous oxide emissions and the stabilization of ammonium following the injection of dairy slurry and digestate in a soil-column experiment. Journal of Plant Nutrition and Soil Science, 183, 129–135. 
IPCC (Intergovernmental Panel on Climate Change). 2014. In: Pachauri R K, Meyer L A, eds. Climate Change 2014: Synthesis Report. Intergovernmental Panel on Climate Change, Geneva, Switzerland. p. 151. 
Ju X, Lu X, Gao Z, Chen X, Su F, Kogge M, Römheld V, Christie P, Zhang F. 2011. Processes and factors controlling N2O production in an intensively managed low carbon calcareous soil under sub-humid monsoon conditions. Environmental Pollution, 159, 1007–1016.
Kou Y P, Wei K, Chen G X, Wang Z Y, Xu H. 2015. Effects of 3, 4-dimethylpyrazole phosphate and dicyandiamide on nitrous oxide emission in a greenhouse vegetable soil. Plant, Soil and Environment, 61, 29–35
Lam S K, Suter H, Mosier A R, Chen D. 2017. Using nitrification inhibitors to mitigate agricultural N2O emission: A double-edged sword? Global Change Biology, 23, 485–489.
Lan T, Suter H, Liu R, Yuan S, Chen D. 2018. Effects of nitrification inhibitors on gross N nitrification rate, ammonia oxidizers, and N2O production under different temperatures in two pasture soils. Environmental Science and Pollution Research, 25, 28344–28354.
Lehtovirta-Morley L E. 2018. Ammonia oxidation: Ecology, physiology, biochemistry and why they must all come together. FEMS Microbiology Letters, 365, fny058. 
Liu C, Liu H, Liu X, Zhang Y, Wang L, Guan D, Al-Kaisi M M, Li Z, Zhang M. 2021. Nitrification inhibitor 3,4-dimethylpyrazole phosphate (DMPP) reduces N2O emissions by altering the soil microbial community in a wheat–maize rotation on the North China Plain. European Journal of Soil Science, 72, 1270–1291.
Luchibia A O, Lam S K, Suter H, Chen Q, O’Mara B, He J Z. 2020. Effects of repeated applications of urea with DMPP on ammonia oxidizers, denitrifiers, and non-targeted microbial communities of an agricultural soil in Queensland, Australia. Applied Soil Ecology, 147, 103392. 
Menéndez S, Merino P, Pinto M, Gonzalez-Murua C, Estavillo J M. 2009. Effect of N-(n-butyl) thiophosphoric triamide and 3,4 dimethylpyrazole phosphate on gaseous emissions from grasslands under different soil water contents. Journal of Environmental Quality, 38, 27–35. 
Miranda N D, Tuomisto H L, McCulloch M D. 2015. Meta-analysis of greenhouse gas emissions from anaerobic digestion processes in dairy farms. Environmental Science & Technology, 49, 5211–5219. 
MOA (Ministry of Agriculture of China). 2015. Action plan for arable land quality protection and upgrading. [2022-10-14]. http://www.moa.gov.cn/ztzl/mywrfz/gzgh/201511/t20151104_4888677.htm (in Chinese)
Möller K. 2015. Effects of anaerobic digestion on soil carbon and nitrogen turnover, N emissions, and soil biological activity. A review. Agronomy for Sustainable Development, 35, 1021–1041. 
Möller K, Stinner W. 2009. Effects of different manuring systems with and without biogas digestion on soil mineral nitrogen content and on gaseous nitrogen losses (ammonia, nitrous oxides). European Journal of Agronomy, 30, 1–16. 
Mosier A R, Halvorson A D, Reule C A, Liu X J. 2006. Net global warming potential and greenhouse gas intensity in irrigated cropping systems in northeastern Colorado. Journal of Environmental Quality, 35, 1584–1598. 
Nadeem S, Bakken L R, Frostegård Å, Gaby J C, Dörsch P. 2020. Contingent effects of liming on N2O-emissions driven by autotrophic nitrification. Frontiers in Environmental Science, 8, 598513.
Nauer P A, Fest B J, Visser L, Arndt S K. 2018. On-farm trial on the effectiveness of the nitrification inhibitor DMPP indicates no benefits under commercial Australian farming practices. Agriculture, Ecosystems & Environment, 253, 82–89. 
Ouyang Y, Norton J M, Stark J M, Reeve J R, Habteselassie M Y. 2016. Ammonia-oxidizing bacteria are more responsive than archaea to nitrogen source in an agricultural soil. Soil Biology and Biochemistry, 96, 4–15. 
Pereira J, Coutinho J, Fangueiro D, Trindade H. 2015. Nitric oxide and nitrous oxide emissions from cattle-slurry and mineral fertiliser treated with nitrification inhibitor to an agricultural soil: A laboratory approach. Spanish Journal of Agricultural Research, 4, e0305–9. 
Pereira J, Fangueiro D, Chadwick D R, Misselbrook T H, Coutinho J, Trindade H. 2010. Effect of cattle slurry pre-treatment by separation and addition of nitrification inhibitors on gaseous emissions and N dynamics: A laboratory study. Chemosphere, 79, 620–627. 
Prosser J I, Nicol G W. 2012. Archaeal and bacterial ammonia-oxidisers in soil: The quest for niche specialisation and differentiation. Trends in Microbiology, 20, 523–531.
Qiao C, Liu L, Hu S, Compton J E, Greaver T L, Li Q. 2015. How inhibiting nitrification affects nitrogen cycle and reduces environmental impacts of anthropogenic nitrogen input. Global Change Biology, 21, 1249–1257.
Ravishankara A R, Daniel J S, Portmann R W. 2009. Nitrous Oxide (N2O): The dominant ozone-depleting substance emitted in the 21st Century. Science, 326, 123–125.
Ruser R, Schulz R. 2015. The effect of nitrification inhibitors on the nitrous oxide (N2O) release from agricultural soils - A review. Journal of Plant Nutrition and Soil Science, 178, 171–188.
Senbayram M, Chen R, Budai A, Bakken L, Dittert K. 2012. N2O emission and the N2O/(N2O+N2) product ratio of denitrification as controlled by available carbon substrates and nitrate concentrations. Agriculture, Ecosystems & Environment, 147, 4–12. 
Senbayram M, Chen R, Muhling K H, Dittert K. 2009. Contribution of nitrification and denitrification to nitrous oxide emissions from soils after application of biogas waste and other fertilizers. Rapid Communications in Mass Spectrometry, 23, 2489–2498. 
Shi X, Hu H W, Zhu-Barker X, Hayden H, Wang J, Suter H, Chen D, He J Z. 2017. Nitrifier-induced denitrification is an important source of soil nitrous oxide and can be inhibited by a nitrification inhibitor 3,4-dimethylpyrazole phosphate. Environmental Microbiology, 19, 4851–4865. 
Song X, Ju X, Topp C F E, Rees R M. 2019. Oxygen regulates nitrous oxide production directly in agricultural soils. Environmental Science and Technology, 53, 12539–12547.
UNEP (United Nations Environment Programme). 2013. Drawing Down N2O to Protect Climate and the Ozone Layer: A UNEP Synthesis Report, Nairobi, Kenya. pp. 1−57.
Vallejo A, Skiba U M, Garcia-Torres L, Arce A, Lopez-Fernandez S, Sanchez-Martin L. 2006. Nitrogen oxides emission from soils bearing a potato crop as influenced by fertilization with treated pig slurries and composts. Soil Biology and Biochemistry, 38, 2782–2793. 
Verdi L, Kuikman P J, Orlandini S, Mancini M, Napoli M, Dalla Marta A. 2019. Does the use of digestate to replace mineral fertilizers have less emissions of N2O and NH3? Agricultural and Forest Meteorology, 269, 112–118. 
Vilas M P, Verburg K, Thorburn P J, Probert M E, Bonnett G D. 2019. A framework for analysing nitrification inhibition: A case study on 3, 4-dimethylpyrazole phosphate (DMPP). Science of the Total Environment, 672, 846–854.
Wang M, Hu R, Zhao J, Kuzyakov Y, Liu S. 2016. Iron oxidation affects nitrous oxide emissions via donating electrons to denitrification in paddy soils. Geoderma, 271, 173–180.
WMO (World Meteorological Organization). 2018. Greenhouse gas bulletin no.14. [2022-10-14]. https://public.wmo.int/en/resources/library/wmo-greenhouse-gas-bulletin
Wu D, Zhang Y, Dong G, Du Z, Wu W, Chadwick D, Bol R. 2021. The importance of ammonia volatilization in estimating the efficacy of nitrification inhibitors to reduce N2O emissions: A global meta-analysis. Environmental Pollution, 271, 116365.
Yang L, Zhu G, Ju X, Liu R. 2020. How nitrification-related N2O is associated with soil ammonia oxidizers in two contrasting soils in China? Science of the Total Environment, 770, 143212. 
Yin S, Zhang X, Jiang Z, Zhu P, Li C, Liu C. 2017. Inhibitory effects of 3,4-dimethylpyrazole phosphate on CH4 and N2O emissions in paddy fields of subtropical China. International Journal of Environmental Research and Public Health, 14, 1177. 
Zheng X, Mei B, Wang Y, Xie B, Wang Y, Dong H, Xu H, Chen G, Cai Z, Yue J, Gu J, Su F, Zou J, Zhu J. 2008. Quantification of N2O fluxes from soil-plant systems may be biased by the applied gas chromatograph methodology. Plant and Soil, 311, 211–234.
Zhu G, Ju X, Zhang J, Müller C, Rees R M, Thorman R E, Sylvester-Bradley R. 2019. Effects of the nitrification inhibitor DMPP (3,4-dimethylpyrazole phosphate) on gross N transformation rates and N2O emissions. Biology and Fertility of Soils, 55, 603–615. 
[1] GAO Yue, LUO Jian, SUN Yue, ZHANG Hua-wei, ZHANG Da-xia, LIU Feng, MU Wei, LI Bei-xing. Photosensitivity and a precise combination of size-dependent lambda-cyhalothrin microcapsules synergistically generate better insecticidal efficacy [J]. >Journal of Integrative Agriculture, 2023, 22(5): 1477-1488.
[2] SHI Wen-xuan, ZHANG Qian, LI Lan-tao, TAN Jin-fang, XIE Ruo-han, WANG Yi-lun. Hole fertilization in the root zone facilitates maize yield and nitrogen utilization by mitigating potential N loss and improving mineral N accumulation[J]. >Journal of Integrative Agriculture, 2023, 22(4): 1184-1198.
[3] HAN Yu-ling, GUO Dong, MA Wei, GE Jun-zhu, LI Xiang-ling, Ali Noor MEHMOOD, ZHAO Ming, ZHOU Bao-yuan. Strip deep rotary tillage combined with controlled-release urea improves the grain yield and nitrogen use efficiency of maize in the North China Plain[J]. >Journal of Integrative Agriculture, 2022, 21(9): 2559-2576.
[4] TIAN Chang, SUN Ming-xue, ZHOU Xuan, LI Juan, XIE Gui-xian, YANG Xiang-dong, PENG Jian-wei. Increase in yield and nitrogen use efficiency of double rice with long-term application of controlled-release urea[J]. >Journal of Integrative Agriculture, 2022, 21(7): 2106-2118.
[5] ZHANG Xiang, ZHOU Ming-yuan, LI Ya-bing, LIU Zhen-yu, CHEN Yuan, CHEN De-hua. Nitrogen spraying affects seed Bt toxin concentration and yield in Bt cotton[J]. >Journal of Integrative Agriculture, 2021, 20(5): 1229-1238.
[6] ZHU Cong-hua, OUYANG Yu-yuan, DIAO You, YU Jun-qi, LUO Xi, ZHENG Jia-guo, LI Xu-yi. Effects of mechanized deep placement of nitrogen fertilizer rate and type on rice yield and nitrogen use efficiency in Chuanxi Plain, China[J]. >Journal of Integrative Agriculture, 2021, 20(2): 581-592.
[7] ZHANG Shui-qin, YUAN Liang, LI Wei, LIN Zhi-an, LI Yan-ting, HU Shu-wen, ZHAO Bing-qiang. Effects of urea enhanced with different weathered coal-derived humic acid components on maize yield and fate of fertilizer nitrogen[J]. >Journal of Integrative Agriculture, 2019, 18(3): 656-666.
[8] LU Yong-li, KANG Ting-ting, GAO Jing-bo, CHEN Zhu-jun, ZHOU Jian-bin. Reducing nitrogen fertilization of intensive kiwifruit orchards decreases nitrate accumulation in soil without compromising crop production[J]. >Journal of Integrative Agriculture, 2018, 17(06): 1421-1431.
[9] ZHAO Li-juan, XIE Jing-fang, ZHANG Hong, WANG Zhen-tao, JIANG Hong-jin, GAO Shao-long . Enzymatic activity and chlorophyll fluorescence imaging of maize seedlings (Zea mays L.) after exposure to low doses of chlorsulfuron and cadmium[J]. >Journal of Integrative Agriculture, 2018, 17(04): 826-836.
[10] HU Mao-long, PU Hui-ming, GAO Jian-qin, LONG Wei-hua, CHEN Feng, ZHOU Xiao-ying, ZHANG Wei, PENG Qi, CHEN Song, ZHANG Jie-fu. Inheritance and molecular characterization of resistance to AHAS-inhibiting herbicides in rapeseed[J]. >Journal of Integrative Agriculture, 2017, 16(11): 2421-2433.
[11] YIN Min-hua, LI Yuan-nong, XU Yuan-bo. Comparative effects of nitrogen application on growth and nitrogen use in a winter wheat/summer maize rotation system[J]. >Journal of Integrative Agriculture, 2017, 16(09): 2062-2072.
[12] HUANG Jing, DUAN Ying-hua, XU Ming-gang, ZHAI Li-mei, ZHANG Xu-bo, WANG Bo-ren, ZHANG Yang-zhu, GAO Su-duan, SUN Nan. Nitrogen mobility, ammonia volatilization, and estimated leaching loss from long-term manure incorporation in red soil[J]. >Journal of Integrative Agriculture, 2017, 16(09): 2082-2092.
[13] WANG Cai-bin, ZHENG Yong-mei, SHEN Pu, ZHENG Ya-ping, WU Zheng-feng, SUN Xue-wu, YU Tian-yi, FENG Hao. Determining N supplied sources and N use efficiency for peanut under applications of four forms of N fertilizers labeled by isotope 15N[J]. >Journal of Integrative Agriculture, 2016, 15(2): 432-439.
[14] SUN Bin-feng, ZHAO Hong, Lü Yi-zhong, LU Fei, WANG Xiao-ke. The effects of nitrogen fertilizer application on methane and nitrous oxide emission/uptake in Chinese croplands[J]. >Journal of Integrative Agriculture, 2016, 15(2): 440-450.
[15] LIU Ya-nan, LI Ying-chun, PENG Zheng-ping, WANG Yan-qun, MA Shao-yun, GUO Li-ping, LIN Er-da, HAN Xue. Effects of different nitrogen fertilizer management practices on wheat yields and N2O emissions from wheat fields in North China[J]. >Journal of Integrative Agriculture, 2015, 14(6): 1184-1191.
No Suggested Reading articles found!