Effects of Saline Water Irrigation and N Application Rate on NH3 Volatilization and N use Efficiency in a Drip-Irrigated Cotton Field

详细信息    查看全文

• 作者：Guangwei Zhou ; Wen Zhang ; Lijuan Ma ; Huijuan Guo ; Wei Min…
• 关键词：Saline water ; N application rate ; N leaching ; NH3 volatilization ; Apparent N recovery ; Cotton field
• 刊名：Water, Air, and Soil Pollution
• 出版年：2016
• 出版时间：April 2016
• 年：2016
• 卷：227
• 期：4
• 全文大小：768 KB
• 参考文献：Abalos, D., Sanchez-Martin, L., Garcia-Torres, L., van Groenigen, J. W., & Vallejo, A. (2014). Management of irrigation frequency and nitrogen fertilization to mitigate GHG and NO emissions from drip-fertigated crops. Science of the Total Environment, 490, 880–888.CrossRef
  Ajdary, K., Singh, D. K., Singh, A. K., & Khanna, M. (2007). Modelling of nitrogen leaching from experimental onion field under drip fertigation. Agricultural Water Management, 89, 15–28.CrossRef
  Akhtar, M., Hussain, F., Ashraf, M. Y., Qureshi, T. M., Akhter, J., & Awan, A. R. (2012). Influence of salinity on nitrogen transformations in soil. Communications in Soil Science and Plant Analysis, 43(12), 1674–1683.CrossRef
  Award EI-Karim, A. H., EI-Mahi, Y. E., & EI-Tilip, A. M. (2004). The influence of soil type, salinity and sodicity on ammonia volatilization in soils fertilized with urea. Annals Agricultural Science, Ain Shams University, Cairo, 49(1), 401–411.
  Bar-Tal, A., Fine, P., Yermiyahu, U., Ben-Gal, A., & Hass, A. (2015). Practices that simultaneously optimize water and nutrient use efficiency: Israeli experiences in fertigation and irrigation with treated wastewater. In P. Drechsel, P. Heffer, H. Magen, R. Mikkelsen, & D. Wichelns (Eds.), Managing water and fertilizer for sustainable agricultural intensification (1st ed., pp. 209–241). Paris: International Fertilizer Industry Association (IFA), International Water Management Institute (IWMI), International Plant Nutrition Institute (IPNI), and International Potash Institute (IPI).
  Ben, A. C., Magdich, S., Ben, R. B., Boukhris, M., & Ben, A. F. (2012). Saline water irrigation effects on soil salinity distribution and some physiological responses of field grown Chemlali olive. Journal of Environmental Management, 113, 538–544.CrossRef
  Bosch-Serra, A. D., Yague, M. R., & Teira-Esmatges, M. R. (2014). Ammonia emissions from different fertilizing strategies in Mediterranean rainfed winter cereals. Atmospheric Environment, 84, 204–212.CrossRef
  Bowman, D. C., Devitt, D. A., & Miller, W. W. (2006). The effect of moderate salinity on nitrate leaching from bermuda grass turf: a lysimeter study. Water, Air, and Soil Pollution, 175, 49–60.CrossRef
  Chen, W., Hou, Z., Wu, L., Liang, Y., & Wei, C. (2010). Evaluating salinity distribution in soil irrigated with saline water in arid regions of northwest China. Agricultural Water Management, 97, 2001–2008.CrossRef
  Chen, A., Lei, B., Hu, W., Lu, Y., Mao, Y., Duan, Z., & Shi, Z. (2015). Characteristics of ammonia volatilization on rice grown under different nitrogen application rates and its quantitative predictions in Erhai Lake Watershed, China. Nutrient Cycling in Agroecosystems, 101, 139–152.CrossRef
  Danso, E. O., Abenney-Mickson, S., Sabi, E. B., Plauborg, F., Abekoe, M., Kugblenu, Y. O., Jensen, C. R., & Andersen, M. N. (2015). Effect of different fertilization and irrigation methods on nitrogen uptake, intercepted radiation and yield of okra (Abelmoschus esculentum L.) grown in the Keta Sand Spit of Southeast Ghana. Agricultural Water Management, 147, 34–42.CrossRef
  Dehghanisanij, H., Agassi, M., Anyoji, H., Yamamoto, T., Inoue, M., & Eneji, A. E. (2006). Improvement of saline water use under drip irrigation system. Agricultural Water Management, 85(3), 233–242.CrossRef
  Duan, Z., & Xiao, H. (2000). Effects of soil properties on ammonia volatilization. Soil Science & Plant Nutrition, 46(4), 845–852.CrossRef
  Ellis, R. A., Murphy, J. G., Markovic, M. Z., Vandenboer, T. C., Makar, P. A., Brook, J., & Mihele, C. (2011). The influence of gas-particle partitioning and surface atmosphere exchange on ammonia during BAQS-Met. Atmospheric Chemistry and Physics, 11, 133–145.CrossRef
  Emmett, B. A. (2007). Nitrogen saturation of terrestrial ecosystems: some recent findings and their implications for our conceptual framework. Water, Air, & Soil Pollution: Focus, 7(1–3), 99–109.CrossRef
  FAO, & IFA. (2001). Global estimates of gaseous emissions of NH 3 , NO and N 2 O from agricultural land. Rome: Food and Agriculture Organization of the United Nations (FAO) and International Fertilizer Industry Association (IFA).
  Fernández, F. G., Terry, R. E., & Coronel, E. G. (2015). Nitrous oxide emissions from anhydrous ammonia, urea, and polymer-coated urea in Illinois cornfields. Journal of Environmental Quality, 44, 415–422.CrossRef
  Flowers, T. J. (2004). Improving crop salt tolerance. Journal of Experimental Botany, 55, 307–319.CrossRef
  Fu, X., Wang, S. X., Ran, L. M., Pleim, J. E., Cooter, E., Bash, J. O., Benson, V., & Hao, J. M. (2015). Estimating NH3 emissions from agricultural fertilizer application in China using the bi-directional CMAQ model coupled to an agro-ecosystem model. Atmospheric Chemistry and Physics, 15, 6637–6649.CrossRef
  Ghaly, A. E., & Ramakrishnan, V. V. (2015). Nitrogen sources and cycling in the ecosystem and its role in air, water and soil pollution: a critical review. Journal of Pollution Effects & Control, 3, 136. doi:10.​4172/​2375-4397.​1000136 .
  Ghanem, M. E., van Elteren, J., Albacete, A., Quinet, M., Martínez-Andújar, C., Kinet, J. M., & Lutts, S. (2009). Impact of salinity on early reproductive physiology of tomato (Solanum lycopersicum) in relation to a heterogeneous distribution of toxic ions in flower organs. Functional Plant Biology, 36, 125–136.CrossRef
  Han, K., Zhou, C., & Wang, L. (2014). Reducing ammonia volatilization from maize fields with separation of nitrogen fertilizer and water in an alternating furrow irrigation system. Journal of Integrative Agriculture, 13(5), 1099–1112.CrossRef
  Hanson, B. R., Simunek, J., & Hopmans, J. W. (2006). Evaluation of urea–ammonium–nitrate fertigation with drip irrigation using numerical modeling. Agricultural Water Management, 86, 102–113.CrossRef
  Haynes, R. J. (1985). Principles of fertilizer use for trickle irrigated crops. Fertilizer Research, 6, 235–255.CrossRef
  Huo, Q., Cai, X., Kang, L., Zhang, H., Song, Y., & Zhu, T. (2015). Estimating ammonia emissions from a winter wheat cropland in North China Plain with field experiments and inverse dispersion modeling. Atmospheric Environment, 104, 1–10.CrossRef
  Jambert, C., Serca, D., & Delmas, R. (1997). Quantification of N-losses as NH3, NO, and N2O and N2 from fertilized maize fields in southwestern France. Nutrient Cycling in Agroecosystems, 48, 91–104.CrossRef
  Jia, X., Shao, L., Liu, P., Zhao, B., Gu, L., Dong, S., Bing, S. H., Zhang, J., & Zhao, B. (2014). Effect of different nitrogen and irrigation treatments on yield and nitrate leaching of summer maize (Zea mays L.) under lysimeter conditions. Agricultural Water Management, 137, 92–103.CrossRef
  Letey, J., & Feng, G. L. (2007). Dynamic versus steady-state approaches to evaluate irrigation management of saline waters. Agricultural Water Management, 91, 1–10.CrossRef
  Li, D. (2013). Emissions of NO and NH3 from a typical vegetable-land soil after the application of chemical N fertilizers in the Pearl River Delta. Plos One, 8(3), e59360. doi:10.​1371/​journal.​pone.​0059360 .CrossRef
  Liao, L., Shao, X., Ji, R., Wen, T., & Xu, J. (2015). Ammonia volatilization from direct seeded later-rice fields as affected by irrigation and nitrogen managements. International Journal of Agriculture and Biology, 17, 582–588.CrossRef
  Lin, Z. C., Dai, Q. G., Ye, S. C., Wu, F. G., Jia, Y. S., Chen, J. D., & Wei, H. Y. (2012). Effects of nitrogen application levels on ammonia volatilization and nitrogen utilization during rice growing season. Rice Science, 19, 125–134.CrossRef
  Liu, M., Liang, R., Zhan, F., Liu, Z., & Niu, A. (2006). Synthesis of slow-release and super absorbent nitrogen fertilizer and its properties. Advances in Polymer Technology, 17, 430–438.CrossRef
  Liu, R., Kang, Y., Zhang, C., Pei, L., Wan, S., Jiang, S., Liu, S., Ren, Z., & Yang, Y. (2014). Chemical fertilizer pollution control using drip fertigation for conservation of water quality in Danjiangkou Reservoir. Nutrient Cycling in Agroecosystems, 98, 295–307.CrossRef
  Liyanage, L. R. M. C., Jayakody, A. N., & Gunaratne, G. P. (2014). Ammonia volatilization from frequently applied fertilizers for the low-country tea growing soils of Sri Lanka. Tropical Agriculture Research Series, 26(1), 48–61.CrossRef
  Lodhi, A., Arshad, M., Azam, F., Sajjad, M. H., & Ashraf, M. (2009). Changes in mineral and mineralizable N of soil incubated at varying salinity, moisture and temperature regimes. Pakistan Journal of Botany, 41, 967–980.
  Mai, V. T., Van, K. H., & Roetter, R. (2010). Nitrogen leaching in intensive cropping systems in Tam Duong district, Red River Delta of Vietnam. Water, Air, and Soil Pollution, 210, 15–31.CrossRef
  Malhi, S. S., Gill, K. S., Harapiak, J. T., Nyborg, M., Gregorich, E. G., & Monreal, C. M. (2003). Light fraction organic N, ammonium, nitrate and total N in a thin Black Chernozemic soil under bromegrass after 27 annual applications of different N rates. Nutrient Cycling in Agroecosystems, 65, 201–210.CrossRef
  Martínez-Alcántara, B., Quiñones, A., Forner-Giner, M. Á., Iglesias, D. J., Primo-Millo, E., & Legaz, F. (2012). Impact of fertilizer-water management on nitrogen use efficiency and potential nitrate leaching in citrus trees. Soil Science & Plant Nutrition, 58, 659–669.CrossRef
  Matson, P., Lohse, K. A., & Hall, S. J. (2002). The globalization of nitrogen deposition: consequences for terrestrial ecosystems. Ambio, 31, 113–119.CrossRef
  McClung, G., & Frankenberger, W. T. (1985). Soil nitrogen transformations as affected by salinity. Soil Science, 139(5), 405–411.
  Merchán, D., Causapéa, J., Abrahão, R., & García-Garizábal, I. (2015). Assessment of a newly implemented irrigated area (Lerma Basin, Spain) over a 10-year period. II: Salts and nitrate exported. Agricultural Water Management, 158, 288–296.CrossRef
  Min, W., Hou, Z., Ma, L., Zhang, W., Ru, S., & Ye, J. (2014). Effects of water salinity and N application rate on water- and N-use efficiency of cotton under drip irrigation. Journal of Arid Land, 6(4), 454–467.CrossRef
  Min, W., Guo, H., Zhang, W., Zhou, G., Ma, L., Ye, J., Liang, Y., & Hou, Z. (2016). Response of soil microbial community and diversity to increasing water salinity and nitrogen fertilization rate in an arid soil. Acta Agriculturae Scandinavica Section B Soil and Plant Science, 66(2), 117–126.
  Munns, R., & Tester, M. (2008). Mechanisms of salinity tolerance. Annual Review of Plant Biology, 59, 651–681.CrossRef
  Munns, R., James, R. A., & Läuchli, A. (2006). Approaches to increasing the salt tolerance of wheat and other cereals. Journal of Experimental Botany, 57, 1025–1043.CrossRef
  Ni, K., Pacholski, A., & Kage, H. (2014). Ammonia volatilization after application of urea to winter wheat over 3 years affected by novel urease and nitrification inhibitors. Agriculture, Ecosystems and Environment, 197, 184–194.CrossRef
  Pan, C., Liu, C., Zhao, H., & Wang, Y. (2013). Changes of soil physico-chemical properties and enzyme activities in relation to grassland salinization. European Journal of Soil Biology, 55, 13–19.
  Peng, X., Maharjan, B., Yu, C., Su, A., Jin, V., & Ferguson, R. B. (2015). A laboratory evaluation of ammonia volatilization and nitrate leaching following nitrogen fertilizer application on a coarse-textured soil. Agronomy Journal, 107(3), 871–879.CrossRef
  Phoga, V., Skewes, M. A., Cox, J. W., Sanderson, G., Alam, J., & Šimunek, J. (2014). Seasonal simulation of water, salinity and nitrate dynamics under drip irrigated mandarin (Citrus reticulata) and assessing management options for drainage and nitrate leaching. Journal of Hydrology, 513, 504–516.CrossRef
  Ramos, T. B., Simunek, J., Goncalves, M. C., Martins, J. C., Prazeres, A., & Pereira, L. S. (2012). Two-dimensional modeling of water and nitrogen fate from sweet sorghum irrigated with fresh and blended saline waters. Agricultural Water Management, 111, 87–104.CrossRef
  Rochette, P., Angers, D. A., Chantigny, M. H., Gasser, M. O., MacDonald, J. D., Pelster, D. E., & Bertrand, N. (2013a). Ammonia volatilization and nitrogen retention: how deep to incorporate urea? Journal of Environmental Quality, 42, 1635–1642.CrossRef
  Rochette, P., Angers, D. A., Chantigny, M. H., Gasser, M. O., MacDonald, J. D., Pelster, D. E., & Bertrand, N. (2013b). NH3 volatilization, soil NH4 + concentration and soil pH following subsurface banding of urea at increasing rates. Canadian Journal of Soil Science, 93, 261–268.CrossRef
  Shalhevet, J. (1994). Using water of marginal quality for crop production: major issues. Agricultural Water Management, 25(3), 233–269.CrossRef
  Shan, L., He, Y., Chen, J., Huang, Q., & Wang, H. (2015). Ammonia volatilization from a Chinese cabbage field under different nitrogen treatments in the Taihu Lake Basin, China. Journal of Environmental Sciences, 38, 14–23.CrossRef
  Singh, A. (2014). Poor quality water utilization for agricultural production: an environmental perspective. Land Use Policy, 43, 259–262.CrossRef
  Singh, K. (2015). Microbial and enzyme activities of saline and sodic soils. Land Degradation and Development. doi:10.​1002/​ldr.​2385 .
  Sommer, S. G., Schjoerring, K., & Denmead, O. T. (2004). Ammonia emission from mineral fertilizers and fertilized crops. Advances in Agronomy, 82, 557–622.CrossRef
  Tian, G., Cai, Z., Cao, J., & Li, X. (2001). Factors affecting ammonia volatilisation from a rice–wheat rotation system. Chemosphere, 42(2), 123–129.CrossRef
  Tripathi, S., Chakraborty, A., Chakrabarti, K., & Bandyopadhyay, B. K. (2007). Enzyme activities and microbial biomass in coastal soils of India. Soil Biology and Biochemistry, 39, 2840–2848.CrossRef
  Wang, J., Wang, D., Zhang, G., & Wang, C. (2012). Effect of wheat straw application on ammonia volatilization from urea applied to a paddy field. Nutrient Cycling in Agroecosystems, 94, 73–84.CrossRef
  Wang, Z., Li, J., & Li, Y. (2014). Simulation of nitrate leaching under varying drip system uniformities and precipitation patterns during the growing season of maize in the North China Plain. Agricultural Water Management, 142, 19–28.CrossRef
  Wang, Q., Huo, Z., Zhang, L., Wang, J., & Zhao, Y. (2016). Impact of saline water irrigation on water use efficiency and soil salt accumulation for spring maize in arid regions of China. Agricultural Water Management, 163, 125–138.CrossRef
  White, R. E., Cai, G., Chen, D., Fan, X. H., Pacholski, A., Zhu, Z. L., & Ding, H. (2002). Gaseous nitrogen losses from urea applied to maize on a calcareous fluvo-aquic soil in the North China Plain. Australian Journal of Soil Research, 40(5), 737–748.CrossRef
  Wu, W., & Ma, B. (2015). Integrated nutrient management (INM) for sustaining crop productivity and reducing environmental impact: A review. Science of the Total Environment, 512–513, 415–427.CrossRef
  Zhang, D., Li, W., Xin, C., Tang, W., Eneji, A. E., & Dong, H. (2012). Lint yield and nitrogen use efficiency of field-grown cotton vary with soil salinity and N rate. Field Crops Research, 138, 63–70.CrossRef
  
• 作者单位：Guangwei Zhou (1)
  Wen Zhang (1)
  Lijuan Ma (1)
  Huijuan Guo (1)
  Wei Min (1)
  Qi Li (1)
  Na Liao (1)
  Zhenan Hou (1)
  
  1. Department of Resources and Environmental Science, Agriculture College, Shihezi University, Box 425, Shihezi, Xinjiang, 832003, People’s Republic of China
  
• 刊物类别：Earth and Environmental Science
• 刊物主题：Environment
  Environment
  Atmospheric Protection, Air Quality Control and Air Pollution
  Waste Water Technology, Water Pollution Control, Water Management and Aquatic Pollution
  Terrestrial Pollution
  Hydrogeology
  
• 出版者：Springer Netherlands
• ISSN：1573-2932

文摘

Ammonia (NH₃) volatilization is one of the main pathways of N loss from farmland soil. Saline water irrigation can have direct or indirect effects on soil NH₃ volatilization, N leaching, and crop N uptake. This study was conducted to evaluate the effects of irrigation water salinity and urea-N application rate on NH₃ volatilization and N use efficiency in a drip-irrigated cotton field. The experiment consisted of three levels of irrigation water salinity: fresh water, brackish water, and saline water (electrical conductivities of 0.35, 4.61, and 8.04 dS/m, respectively). The N application rates were 0, 240, 360, and 480 kg/ha. The results showed that soil salinity and soil moisture content were significantly higher in the saline water treatment than in either the fresh or brackish water treatments. Irrigation water salinity significantly increased soil NH₄-N concentration, but NO₃-N concentration decreased as water salinity increased. The amount of N leaching varied from 5.0 to 25.5 kg/ha, accounting for 1.81 to 4.79 % of the urea-N applied under different water salinity and N application rate treatments. Both the amount of N leaching and the proportions of applied N lost through leaching significantly increased as water salinity increased. N application increased the amounts of N leaching, but the ratios of applied N were not affected by N application rate. Soil NH₃ volatilization increased rapidly after urea fertigation, and peaked at 1–2 days after N application, then decreased rapidly. The amount of NH₃ volatilization varied from 9.0 to 33.7 kg/ha, accounting for 3.2 to 3.8 % of the N applied in all treatments. Soil NH₃ volatilization was significantly higher in the saline water treatment than that in either the fresh or the brackish water treatments. Cotton N uptake increased significantly as N application rate increased, but decreased with irrigation water salinity increased. In conclusion, saline water irrigation with high N application rate induced high N leaching and NH₃ volatilization losses, thereby dramatically reducing the apparent N recovery (ANR) of cotton.