Volatile loss of nitrogen during decomposition of legume green manure

Abstract Significant amounts of volatile ammonia (NH3) may be lost from agricultural ecosystems. While NH3 volatilization from fertilizers has been well-documented, corresponding losses from crop residues, particularly legume green manures, have not been adequately quantified. Ammonia losses from decomposing lentil (Lens culinaris Medik.) green manure were measured under controlled conditions by applying residue to soil inside sealed chambers, establishing air flow and periodically measuring accumulated NH3 loss using acid traps. Three consecutive experiments were conducted to determine the effect of residue placement, air flow rate and green manure composition, respectively. The first experiment, using a relatively slow flow rate (0.07 chamber displacements min−1), demonstrated significant volatilization of NH3 (5% of applied N after 56 days) from green manure placed on or suspended above the soil. Incorporating the green manure into soil almost eliminated NH3 losses. Drying and rewetting the residues after the initial 28 days had only a small stimulatory effect on subsequent volatile losses. A second experiment indicated that maximum volatilization could be achieved at air flow rates of 0.3 chamber displacements min−1 or higher. A third experiment, using an optimum flow rate (0.5 displacements min−1), demonstrated significantly higher volatile N losses from field-grown lentil material (14% over 14 days) than from hydroponically cultured lentil material (8% over 14 days). This difference was attributed, in part, to higher soluble N concentrations in the former residue. Ammonia volatilization consistently demonstrated similar temporal patterns: a rapid initial flush, apparently from the ammonification of labile N. followed by an indefinite period of slow volatilization, probably from the mineralization of more recalcitrant N fractions. The volatile loss of labile N from decomposing green manure may appreciably diminish its fertility benefit and represent an important contribution to atmospheric N concentrations.

[1]  G. S. Campbell,et al.  Role of available carbon and nitrogen in determining the rate of wheat straw decomposition , 1984 .

[2]  D. Whitehead,et al.  The volatilization of ammonia from perennial ryegrass during decomposition, drying and induced senescence , 1988 .

[3]  G. F. Arkin,et al.  Design and Test of a Field Sampler for Ammonia Volatilization , 1977 .

[4]  E. Craswell,et al.  Isotopic studies of the nitrogen balance in a cracking clay. I. Recovery of added nitrogen from soil and wheat in the glasshouse and gas lysimeter , 1975 .

[5]  W. V. Bartholomew,et al.  Some Aspects of Ammonia Sorption by Soil Surfaces 1 , 1964 .

[6]  R. Hauck Agronomic and technological approaches to minimizing gaseous nitrogen losses from croplands , 1983 .

[7]  R. Kimber Phytotoxicity from plant residues. I. The influence of rotted wheat straw on seedling growth , 1967 .

[8]  H. Janzen,et al.  FATE OF N APPLIED AS GREEN MANURE OR AMMONIUM FERTILIZER TO SOIL SUBSEQUENTLY CROPPED WITH SPRING WHEAT AT THREE SITES IN WESTERN CANADA , 1990 .

[9]  L. F. Elliott,et al.  Volatilization of Nitrogen-Containing Compounds from Beef Cattle Areas1 , 1971 .

[10]  M. S. Smith,et al.  Tillage Effects on Nitrogen Recovery by Corn from a Nitrogen‐15 Labeled Legume Cover Crop , 1989 .

[11]  D. Whitehead,et al.  Volatilization of ammonia from urea applied to soil: Influence of hippuric acid and other constituents of livestock urine , 1989 .

[12]  T. McCalla,et al.  Loss of Carbon Dioxide and Ammonia from Crop Residues during Decomposition , 1946 .

[13]  R. B. Jackson,et al.  Decomposition of plant material in Australian soils. II. Residual organic 14C and 15N from legume plant parts decomposing under field and laboratory conditions , 1984 .

[14]  I. Galbally,et al.  The fate of nitrogen compounds in the atmosphere , 1983 .

[15]  J. R. Simpson,et al.  Volatilization of ammonia , 1983 .

[16]  A. Cogle,et al.  Carbon transformations during wheat straw decomposition , 1989 .

[17]  D. Whitehead,et al.  Decomposing grass herbage as a source of ammonia in the atmosphere , 1989 .

[18]  H. Chapman,et al.  VOLATILIZATION OF AMMONIA FROM SURFACE‐FERTILIZED SOILS , 1951 .

[19]  G. Farquhar,et al.  Gaseous nitrogen losses from plants , 1983 .

[20]  D. R. Lockyer,et al.  Evaluation of a system of wind tunnels for field studies of ammonia loss from grassland through volatilisation , 1985 .

[21]  G. Farquhar,et al.  Ammonia Volatilization from Senescing Leaves of Maize , 1979, Science.

[22]  D. W. Nelson Gaseous Losses of Nitrogen Other Than Through Denitrification , 2015 .

[23]  D. Möller,et al.  A relationship between agricultural NH3 emissions and the atmospheric SO2 content over industrial areas , 1985 .

[24]  J. Stewart,et al.  An improved method for the determination of carbon in soils and soil extracts by dry combustion , 1981 .

[25]  R. Haynes,et al.  Chapter 5 – Gaseous Losses of Nitrogen , 1986 .

[26]  W. Kroontje,et al.  Relationships between Ammonia Volatilization, Ammonia Concentration and Water Evaporation 1 , 1964 .

[27]  R. Gilkes,et al.  Leaching of copper and zinc from trace element superphosphate , 1975 .

[28]  R. W. Sheard,et al.  Comparison of Conventional and Automated Procedures for Nitrogen, Phosphorus, and Potassium Analysis of Plant Material Using a Single Digestion1 , 1967 .

[29]  E. Lemon,et al.  Ammonia Exchange at the Land Surface1 , 1980 .

[30]  R. Weiland,et al.  Gaseous Nitrogen Loss from Soybean Foliage1 , 1979 .

[31]  G. L. Terman Volatilization Losses of Nitrogen as Ammonia from Surface-Applied Fertilizers, Organic Amendments, and Crop Residues , 1980 .