How does burning of rice straw affect CH4 and N2O emissions? A comparative experiment of different on-field straw management practices

被引:136
|
作者
Romasanta, Ryan R. [1 ]
Sander, Bjoern Ole [1 ]
Gaihre, Yam Kanta [1 ,3 ]
Alberto, Ma Carmelita [1 ]
Gummert, Martin [1 ]
Quilty, James [1 ]
Van Hung Nguyen [1 ]
Castalone, Angeli Grace [1 ]
Balingbing, Carlito [1 ]
Sandro, Joseph [1 ]
Correa, Teodoro, Jr. [1 ]
Wassmann, Reiner [1 ,2 ]
机构
[1] IRRI, Los Banos, Philippines
[2] Karlsruhe Inst Technol, Inst Meteorol & Climate Res, Garmisch Partenkirchen, Germany
[3] Int Fertilizer Dev Ctr, Dhaka, Bangladesh
关键词
Emission factors; Rice straw burning; Straw management practices; GHG emissions; GWP; METHANE EMISSIONS; AIR-QUALITY; SYSTEM; CARBON; RUMINANTS; IMPROVE; IMPACT;
D O I
10.1016/j.agee.2016.12.042
中图分类号
S [农业科学];
学科分类号
09 ;
摘要
Open-burning of rice straw residues pollutes the air and contributes to global warming through emissions of greenhouse gases (GHGs). Although burning of straw residues emits large amounts of CO2, this component of the smoke is not considered as net GHG emissions and only concludes the annual carbon cycle that has started with photosynthesis. Hence, we focused on emissions of CH4 and N2O from open-field burning against a baseline of straw incorporation. The experimental approach combined a newly designed combustion chamber for the collection of smoke followed by chemical analysis (Exp. A) as well as field observations of soil-borne emissions for different straw treatments (Exp. B). At constant straw moisture of 10%, the mass-scaled Emission Factors (EFm) were 4.51 g CH4 and 0.069 g N2O per kg dry Weight (kg(dw)(-1)) of straw. In Exp. B, we conducted field trials over two seasons with the following straw management practices: SRt straw retained including stubbles and incorporated, PSRm partial straw removal only stubbles incorporated, CSRm complete straw removal including removal of stubbles, and SB straw burned followed by incorporation of ash and unburned residues. Soil-borne emissions were recorded with a closed chamber approach whereas straw burning was computed indirectly using the EF from Exp. A. As metrics for comparison, we have used the GWP contributions of CH4 and N2O for the different straw management practices over two cropping seasons in the field. On an annual basis, SRt had the highest total GWP (8023 kg CO(2)eq ha(-1)). SB entailed a GWP of 4913 kg CO(2)eq ha(-1) that was almost identical to the GWP of PSRm (4531 kg CO(2)eq ha(-1)). CSRm had the lowest GWP (3470 kg CO(2)eq ha(-1)) that Was significantly lower than that of SRt. However, full GHG accounting of straw removed from the field will depend on the ensuing utilization of straw and the off-field emissions involved which was outside of the boundaries of this study. The quantification of open field burning in this study can be instrumental for diverse purposes by providing data of an important component in emission inventories and carbon footprint analysis of rice. (C) 2017 The Authors. Published by Elsevier B.V.
引用
收藏
页码:143 / 153
页数:11
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