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Suppression of NH3 and N2O emissions by massive urea intercalation in montmorillonite

  • SOILS, SEC 1 • SOIL ORGANIC MATTER DYNAMICS AND NUTRIENT CYCLING • RESEARCH ARTICLE
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Abstract

Purpose

A large amount of nitrogen (N) fertilizers has been broadcasted over soil surface for reliable crop production. Unfortunately, the broadcasted N vulnerable to volatilization and leaching can lead to serious environmental problems. As a new approach to mitigate N loss of broadcasted fertilizers, massive intercalation of urea into montmorillonite (MMT) was recently proposed to innovatively enhance the urea use efficiency. This study focuses on demonstrating the behaviors of the urea intercalated into MMT in soils.

Materials and methods

A eutectic Ca0.7/Mg0.3(urea)6Cl2 complex was intercalated into MMT at a weight ratio of complex/MMT of 1.0 (the resulting product was referred to as Ca/Mg-UCM). Behaviors of broadcasted urea were examined on both bare and planted soils. Soil urea-N, ammonium, and nitrate were analyzed using a spectrophotometer after extraction of the soil by 2 M KCl solution. Ammonia emitted from the soil was collected by a closed-dynamic air flow method, and NH3 concentration was determined by titration with a standard 0.005 M H2SO4. In particular, urea labeled with 5% 15N atom was used in evaluating N uptake. Emission of N2O was evaluated by collecting all the gases from the soil using a PVC column.

Results and discussion

A dramatic difference between the urea-broadcasted and Ca/Mg-UCM-broadcasted soils was found in ammonia emission. A peak emission rate decreased from 38.5 N mg m−2 h−1 of the urea-broadcasted soil to 28.3 N mg m−2 h−1 of the Ca/Mg-UCM-broadcasted soil. This remarkable suppression of the initial ammonia emission could be explained by the events such as delayed urea hydrolysis, dissolution of ammonia into soil waters, especially water adsorbed on MMT, adsorption of ammonia by MMT, and delivery of urea molecules into inner soils through deintercalation and diffusion. Uptake amounts of total N and 15N by whole perilla plants were substantially increased by Ca/Mg-UCM broadcasting, compared with urea broadcasting. The intercalation also suppressed N2O emission noticeably. At the same dosage of urea, Ca/Mg-UCM broadcasting led to an increase in dry weight of kale shoot by 38%, compared with urea broadcasting.

Conclusions

This study has successfully demonstrated that the urea intercalation led to considerable suppression of both ammonia and N2O emissions compared to that with urea-broadcasted soils but without any noticeable effects on fast effectiveness of urea in the former. Thus, clay-intercalated urea as a fast effective fertilizer is expected to greatly contribute to mitigation of ammonia and N2O emissions along with green and sustainable crop production.

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References

  • Brigatti MF, Galan E, Theng BKG (2006) Structures and mineralogy of clay minerals: hand book of clay science. In: Bergaya F, Theng BKG, Lagaly G (eds) Developments in clay science 1. Elsevier, Amsterdam, pp 19–86

    Google Scholar 

  • Corniello A, Ducci D, Ruggieri G (2007) Areal identification of groundwater nitrate contamination sources in Periurban areas. J Soils Sediments 7:159–166

    Article  CAS  Google Scholar 

  • Crawford NM, Glass DM (1998) Molecular and physiological aspects of nitrate uptake in plants. Trends Plant Sci 3:389–395

    Article  Google Scholar 

  • Dontsova KM, Norton LD, Johnston CT (2005) Calcium and magnesium effects on ammonia adsorption by soil clays. Soil Sci Soc Am J 69:1225–1232

    Article  CAS  Google Scholar 

  • Dorich RA, Nelson DW (1983) Direct colorimetric measurement of ammonium in potassiumchloride extracts of soils. Soil Sci Soc Am J 47:833–836

    Article  CAS  Google Scholar 

  • Fageria NK, Baligar VC, Li YC (2008) The role of nutrient efficient plants in improving crop yields in the twenty first century. J Plant Nutr 31:1121–1157

    Article  CAS  Google Scholar 

  • Gruber N, Galloway JN (2008) An earth-system perspective of the global nitrogen cycle. Nature 451:293–296

    Article  CAS  Google Scholar 

  • He ZL, Calvert DV, Alva AK, Li YC, Banks DJ (2002) Clinoptilolite zeolite and cellulose amendments to reduce ammonia volatilization in a calcareous sandy soil. Plant Soil 247:253–260

    Article  CAS  Google Scholar 

  • Hebert CE, Wassenaar LI (2001) Stable nitrogen isotopes in waterfowl feathers reflect agricultural land use in Western Canada. Environ Sci Technol 35:3482–3487

    Article  CAS  Google Scholar 

  • Hermsen K, Garabet S (2003) A comparison of the isotope-dilution and the difference method for estimating fertilizer nitrogen recovery fractions in crops. III. Experimental. NJAS 51(3):237–261

    Google Scholar 

  • Hossain MF, White SK, Elahi SF, Sultana N, Choudhury MHK, Alam QK, Rother JA, Gaunt JL (2005) The efficiency of nitrogen fertilizer for rice in Bangladeshi farmers’ fields. Field Crop Res 93:94–107

    Google Scholar 

  • Khalil MI, Schmidhalter U, Gutser R (2006) N2O, NH3 and NOx emissions as a function of urea granule size and soil type under aerobic conditions. Water Air Soil Poll 175:127–148

    Article  CAS  Google Scholar 

  • Khalil MI, Rosenani AB, Cleemput OV, Boeckx P, Shamshuddin J, Fauziah CI (2002) Nitrous oxide production from an ultisol of the humid tropics treated with different nitrogen sources and moisture regimes. Biol Fertil Soils 36:59–65

    Article  CAS  Google Scholar 

  • Kim KS (2010) Suppression of fertilizer N loss through massive urea intercalation into montmorillonite. PhD thesis. http://dcollection.knu.ac.kr/jsp/index.jsp (Accessed 15 Mar 2010)

  • Kim SD, Dale BE (2008) Effects of nitrogen fertilizer application on greenhouse gas emissions and economics of corn production. Environ Sci Technol 42:6028–6033

    Article  CAS  Google Scholar 

  • Lefsrud M, Kopsell DA, Kopsell DE, Randle WM (2006) Kale carotenoids are unaffected by, whereas biomass production, elemental concentrations, and selenium accumulation respond to, changes in selenium fertility. J Agric Food Chem 54:1764–1771

    Article  CAS  Google Scholar 

  • Jenkins D, Medsker LL (1964) Brucine method for determination of nitrate in ocean, estuarine, and fresh waters. Anal Chem 36:610–612

    Article  CAS  Google Scholar 

  • Machado CMD, Cardoso AA, Allen AG (2008) Atmospheric emission of reactive nitrogen during biofuel ethanol production. Environ Sci Technol 42:381–385

    Article  CAS  Google Scholar 

  • Marschner H (1995) Functions of mineral nutrients:macronutrients:mineral nutrition of higher plants, 2nd edn. Academic Press Inc, San Diego, pp 230–312

    Google Scholar 

  • Mulvaney RL, Bremner JM (1979) A modified diacetyl monoxime method for colorimetric determination of urea in soil extracts. Commun Soil Plant Anal 10:1163–1170

    Article  CAS  Google Scholar 

  • North Willamette Research and Extension Center (2004) Commercial Vegetable Production Guide. Oregon State University: Corvallis, OR, USA http://nwrec.hort.oregonstate.edu/vegindex.html(Accessed 15 Mar 2010)

  • Pan K, Xu Z, T Blumfield, Totua S, Lu M (2008) In situ mineral 15N dynamics and fate of added 15NH4 + in hoop pine plantation and adjacent native forest in subtropical Australia. J Soils Sediments 8:398–405

    Article  CAS  Google Scholar 

  • Park M, Kim CY, Lee DH, Choi CL, Choi J, Lee S-R, Choi J-H (2004) Intercalation of magnesium-urea complex into swelling clay. J Phys Chem Solids 65:409–412

    Article  CAS  Google Scholar 

  • Rehm G (2009) Soil cation ratios for crop production. North Central Regional Extension Publication 533: University of Minnesota Extension Service. http://www.extension.umn.edu/distribution/cropsystems/ (Accessed 15 Mar 2010)

  • Shah SB, Wolfe ML, Borggaard JT (2004) Simulating the fate of subsurface-banded urea. Nutr Cycl Agroecosyst 70:47–66

    Article  CAS  Google Scholar 

  • Siva KB, Aminuddin H, Husni MHA, Manas AR (1999) Ammonia volatilization from urea as affected by tropical-based palm oil palm effluent (pome) and peat. Commun Soil Sci Plant Anal 30:785–804

    Article  CAS  Google Scholar 

  • Sommer SG, Scjoerring JK, Denmead OT (2004) Ammonia emission from mineral fertilizers and fertilized crops. Adv Agron 82:557–622

    Article  CAS  Google Scholar 

  • Wang W-H, KÖhler B, Cao F-Q, Liu L-H (2008) Molecular and physiological aspects of urea transport in high plants. Plant Sci 175:467–477

    Article  CAS  Google Scholar 

  • Yuping Y, Liqing S, Min C, Zheng Z, Jianwei T, Yinghong W, Yiping Z, Rui W, Guangren L, Yuesi W, Yang S (2008) Fluxes of CH4 and N2O from soil under a tropical seasonal rain forest in Xishuangbanna, Southwest China. J Environ Sci-China 20:207–215

    Google Scholar 

  • Zaman M, Nguyen ML, Blennerhassertt JD, Quin BF (2008) Reducing NH3, N2O and NO3 -N losses from a pasture soil with urease or nitrification inhibitors and elemental S-amended nitrogenous fertilizers. Biol Fertil Soils 44:693–705

    Article  CAS  Google Scholar 

Download references

Acknowledgments

This study was supported by Technology Development Program for Agriculture and Forestry (No. 106135-3), Ministry for Agriculture, Forestry and Fisheries, Republic of Korea.

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Correspondence to Man Park or Hee-Myong Ro.

Additional information

Communicated by Zucong Cai

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The online version of this article contains supplementary material, which is available to authorized users.

Table S1

Physicochemical properties of the soil used in this study (DOC 27.0 kb)

Table S2

Dry weight of perilla plants grown for 12 days after broadcasting (DOC 27.5 kb)

Table S3

Effect of the intercalation on yield of kale leaf cultivated in a greenhouse at Gyeongsangbuk-do Agricultural Rural Research & Extension Services in Korea (DOC 28.0 kb)

Fig. S1

Images of perilla leaves exposed to the gases emitted from broadcasted urea. Each pot was broadcasted with an application rate of 200 mg urea/100 g soil. The pots were covered with a vinyl film and maintained at a temperature range of 27 ~ 35°C for 1 day after broadcasting. Urea broadcasting resulted in severe wilting of perilla leaves due to ammonia toxicity (DOC 55.0 kb)

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Kim, K.S., Park, M., Choi, C.L. et al. Suppression of NH3 and N2O emissions by massive urea intercalation in montmorillonite. J Soils Sediments 11, 416–422 (2011). https://doi.org/10.1007/s11368-010-0326-z

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  • DOI: https://doi.org/10.1007/s11368-010-0326-z

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