Please wait a minute...
Journal of Integrative Agriculture  2015, Vol. 14 Issue (12): 2426-2433    DOI: 10.1016/S2095-3119(15)61168-6
Special Focus: Best Soil Management from Long-Term Field Experiments for Sustainable Agriculture Advanced Online Publication | Current Issue | Archive | Adv Search |
Determination of optimum nitrogen application rates in Zhejiang Province, China, based on rice yields and ecological security
 LI Yan, CHEN Yi, WU Chun-yan, TANG Xu, JI Xiao-jiang
Institute of Environment Resource and Soil Fertilizer, Zhejiang Academy of Agricultural Sciences, Hangzhou 310021, P.R.China
Download:  PDF in ScienceDirect  
Export:  BibTeX | EndNote (RIS)      
摘要  Excessive nitrogen (N) fertilization in intensive agricultural areas such as the plain region of South China has resulted in low nitrogen use efficiency and serious environmental problems. To determine the optimum N application rate, grain yield, apparent nitrogen recovery efficiency (ANRE), apparent N loss, and ammonium (NH3) volatilization under different N application rates in the three years from 2012 to 2014 were studied. The results showed that the relationship between grain yields and N application rate in the three years were well fitted by quadratic equations. When N application rate reached 197 kg ha–1 in 2012, 199 kg ha–1 in 2013 and 196 kg ha–1 in 2014, the plateau of the grain yields appeared. With the increase of N application rate, the ANRE for rice decreased which could be expressed with sigmoidal equation; when N application rate was 305 kg ha–1 in 2012, 275 kg ha–1 in 2013 and 312 kg ha–1 in 2014, the curves of ANRE appeared turing points. Besides, the relationship between soil Nresidual and N application rate was fitted by the quadratic equation and the maximums of soil Nresidual were reached in the three years with the N application rate of 206, 244 and 170 kg ha–1, respectively. Statistical analysis indicated that NH3 volatilization and apparent N loss in three years all increased with the increasing N application rate. When the amount of NH3 volatilization increased to 11.6 kg N ha–1 in 2012, 40.5 kg N ha–1 in 2013 and 57.0 kg N ha–1 in 2014, the apparent N loss in the three years had obvious increase. To determine the optimum N application rate, the average N application on the plateau of the grain yield was considered as the lower limit while the average N application rate at the turning points of ANRE, the residual N in soil and apparent N loss was taken as the upper limit. According to the results in three years, the optimum N application rate for rice in Zhejiang was 197–255 kg ha–1.

Abstract  Excessive nitrogen (N) fertilization in intensive agricultural areas such as the plain region of South China has resulted in low nitrogen use efficiency and serious environmental problems. To determine the optimum N application rate, grain yield, apparent nitrogen recovery efficiency (ANRE), apparent N loss, and ammonium (NH3) volatilization under different N application rates in the three years from 2012 to 2014 were studied. The results showed that the relationship between grain yields and N application rate in the three years were well fitted by quadratic equations. When N application rate reached 197 kg ha–1 in 2012, 199 kg ha–1 in 2013 and 196 kg ha–1 in 2014, the plateau of the grain yields appeared. With the increase of N application rate, the ANRE for rice decreased which could be expressed with sigmoidal equation; when N application rate was 305 kg ha–1 in 2012, 275 kg ha–1 in 2013 and 312 kg ha–1 in 2014, the curves of ANRE appeared turing points. Besides, the relationship between soil Nresidual and N application rate was fitted by the quadratic equation and the maximums of soil Nresidual were reached in the three years with the N application rate of 206, 244 and 170 kg ha–1, respectively. Statistical analysis indicated that NH3 volatilization and apparent N loss in three years all increased with the increasing N application rate. When the amount of NH3 volatilization increased to 11.6 kg N ha–1 in 2012, 40.5 kg N ha–1 in 2013 and 57.0 kg N ha–1 in 2014, the apparent N loss in the three years had obvious increase. To determine the optimum N application rate, the average N application on the plateau of the grain yield was considered as the lower limit while the average N application rate at the turning points of ANRE, the residual N in soil and apparent N loss was taken as the upper limit. According to the results in three years, the optimum N application rate for rice in Zhejiang was 197–255 kg ha–1.
Keywords:  optimum nitrogen application rate       Zhejiang       rice yields       ecological security  
Received: 09 June 2015   Accepted:
Fund: 

This research was supported by the National Natural Science Foundation of China (41501238), the Key Technologies R&D Program of China during the 12th Five-Year Plan period (2015BAD23B03) and the Special Fund for Agro-scientific Research in the Public Interest from the Ministry of Agriculture, China (201003014-02-08).

Corresponding Authors:  WU Chun-yan, Tel/Fax: +86-571-86404269,E-mail: wuchyan2012@163.com     E-mail:  wuchyan2012@163.com
About author:  LI Yan, E-mail: liyann0410@163.com;

Cite this article: 

LI Yan, CHEN Yi, WU Chun-yan, TANG Xu, JI Xiao-jiang. 2015. Determination of optimum nitrogen application rates in Zhejiang Province, China, based on rice yields and ecological security. Journal of Integrative Agriculture, 14(12): 2426-2433.

Alivelu K, Srivastava S, Subba Rao A, Singh K N, SelvakumariG, Raju N S. 2003. Comparison of modified mitscherlichand response plateau models for calibrating soil test basednitrogen recommendations for rice on Typic Ustropept.Communications in Soil Science and Plant Analysis, 34,2633-2643

Alivelu K, Subba R A, Sanjay S, Singh K N, Raju N S, Madhuri P.2006. Prediction of optimal nitrogen application rate of ricebased on soil test values. European Journal of Agronomy,25, 71-73

Bouwman A F, Boumans L J M, Batjes N H. 2002. Estimationof global NH3 volatilization loss from synthetic fertilizersand animal manure applied to arable lands and grasslands.Global Biogeochemical Cycles, 16, 8-14

Camargo J A, Alonso A. 2006. Ecological and toxicologicaleffects of inorganic nitrogen pollution in aquatic ecosystems:A global assessment. Environment International, 32,831-849

Chen A Q, Lei B K, Lu Y, Mao Y T, Zhang D. 2013. Studyon nitrogen application rate tolerance based on rice yieldand ecological security in hilly areas of South China.Transactions of the Chinese Society of AgriculturalEngineering, 29, 131-139 (in Chinese)

Cui Z L, Zhang F S, Chen X P, Dou Z X, Li J L. 2010. In-seasonnitrogen management strategy for winter wheat: Maximizingyields, minimizing environmental impact in an overfertilizationcontext. Field Crops Research, 116, 140-146

Guo R, Nendel C, Rahn C, Jiang C, Chen Q. 2010. Trackingnitrogen losses in a greenhouse crop rotation experimentin North China using the EU-Rotate N simulation model.Environment Pollution, 158, 2218-2229

ISS, CAS (Institute of Soil Science, Chinese Academy ofSciences). 1978. Physical and Chemical Analytical Methodsof Soil. Shanghai Science Technology Press, Shanghai,China. (in Chinese)

Ju X T, Xing G X, Chen X P, Zhang S L, Zhang L J, Liu XJ, Cui Z L, Yin B, Christie P, Zhu Z L, Zhang F S. 2009.Reducing environmental risk by improving N managementin intensive Chinese agricultural systems. Proceedings ofthe National Academy of Sciences of the United States ofAmerica, 106, 3041-3046

Lang M, Li P, Yan X. 2013. Runoff concentration and loadof nitrogen and phosphorus from a residential area inan intensive agricultural watershed. Science of TotalEnvironment, 458-460, 238–245

Liu L J. 2005. Fertilizer-nitrogen use effenciency and itsregulation approaches in rice. Ph D thesis, YangzhouUniversity, China. (in Chinese)

Liu X J, Ju X T, Zhang F S, Pan J R, Christie P. 2003. Nitrogendynamics and budgets in a winter wheat-maize croppingsystem in the North China Plain. Field Crops Research,83, 111-124

Nelson D W, Sommer L E. 1982. Total carbon, organic carbon,and organic matter. In: Page A L, Miller R H, Keeney DR, eds., Methods of Soil Analysis. American Society ofAgronomy and Soil Science Society of American, Madison,Wisconsin, USA. pp. 539-579

Polychronaki E, Douma C, Giourga C, Loumou A. 2012.Assessing nitrogen fertilization strategies in winter wheatand cotton crops in northern Greece. Pedosphere, 22,689-697

Rajsic P, Weersink A. 2008. Do farmers waste fertilizer? Acomparison of ex post optimal nitrogen rates and ex anterecommendations by model, site, and year. AgriculturalSystems, 97, 56-67

Singh J, Kunhikrishnan A, Bolan NS, Saggar S. 2013. Impactof urease inhibitor on ammonia and nitrous oxide emissionsfrom temperate pasture soil cores receiving urea fertilizerand cattle urine. Science of Total Environment, 465, 56-63

Smith I, Schallenberg M. 2013. Occurrence of the agriculturalnitrification inhibitor, dicyandiamide, in surface watersand its effects on nitrogen dynamics in an experimentalaquatic system. Agriculture, Ecosystem and Environment,164, 23-31

Soares J R, Cantarella H, Menegale M L C. 2012. Ammoniavolatilization losses from surface-applied urea with ureaseand nitrification inhibitors. Soil Biology and Biochemistry,52, 82-89

Song X Z, Zhao C X, Wang X L, Li J. 2009. Study of nitrateleaching and nitrogen fate under intensive vegetableproduction pattern in northern China. Comptes RendusBiologies, 332, 385-392

Su Y Z, Zhang Z H, Yang R. 2007. Amount of irrigation andnitrogen application for maize grown on sandy farmland inthe marginal oasis in the middle of Heihe River Basin. ActaAgronomica Sinica, 33, 2007-2015

Tian G M, Cao J L, Cai Z C, Ren L T. 1998. Ammoniavolatilization from winter wheat field top-dressed with urea.Pedosphere, 8, 331-336

Valkama E, Salo T, Esala M, Turtola E. 2013. Nitrogenbalances and yields of spring cereals as affected bynitrogen fertilization in northern conditions: A meta-analysis.Agriculture, Ecosystem and Environment, 164, 1-13

Wang D J, Liu Q, Lin J H, Sun R J. 2004. Optimum nitrogenuse and reduced nitrogen loss for production of rice andwheat in the Yangtse Delta region, China. EnvironmentalGeochemistry and Health, 26, 221-227

Watkins K B, Hignight J A, Norman R J, Roberts T L, Slaton N A, Wilson Jr C E, Frizzell D L. 2010. Comparison of economicoptimum nitrogen rates for rice in Arkansas. AgronomyJournal, 102, 1099-1108

Welten B G, Ledgard S F, Schipper L A, Waller J E, Kear M J,Dexter M M. 2013. Effects of prolonged oral administrationof dicyandiamide to dairy heifers on excretion in urine andefficacy in soil. Agriculture Ecosystem Environment, 173,28-36

Xia Y Q, Yan X Y. 2012. Ecologically optimal nitrogenapplication rates for rice cropping in the Taihu Lake regionof China. Sustainability Science, 7, 33-44

Yu Q G, Ma J W, Zou P, Lin H, Sun W C, Yin J Z, Fu J R. 2015.Effects of combined application of organic and inorganicfertilizers plus nitrification inhibitor DMPP on nitrogen runoffloss in vegetable soils. Environmental Science and PollutionResearch, 22, 472-481
No related articles found!
No Suggested Reading articles found!