Trade-offs between soil carbon sequestration and reactive nitrogen losses under straw return in global agroecosystems

被引:408
作者
Xia, Longlong [1 ,2 ]
Lam, Shu Kee [3 ]
Wolf, Benjamin [2 ]
Kiese, Ralf [2 ]
Chen, Deli [3 ]
Butterbach-Bahl, Klaus [2 ]
机构
[1] Chinese Acad Sci, Inst Soil Sci, State Key Lab Soil & Sustainable Agr, Nanjing, Jiangsu, Peoples R China
[2] Karlsruhe Inst Technol, Inst Meteorol & Climate Res IMK IFU, Garmisch Partenkirchen, Germany
[3] Univ Melbourne, Sch Agr & Food, Fac Vet & Agr Sci, Melbourne, Vic, Australia
基金
美国国家科学基金会;
关键词
ammonia emission; carbon sequestration; crop productivity; reactive N losses; straw return; trade-off relationship; GREENHOUSE-GAS EMISSION; WHEAT CROPPING SYSTEM; NO-TILL CORN; OXIDE EMISSIONS; ORGANIC-MATTER; AGRICULTURAL SOILS; RESIDUE MANAGEMENT; N2O EMISSIONS; INPUT; MITIGATION;
D O I
10.1111/gcb.14466
中图分类号
X176 [生物多样性保护];
学科分类号
090705 ;
摘要
It is widely recommended that crop straw be returned to croplands to maintain or increase soil carbon (C) storage in arable soils. However, because C and nitrogen (N) biogeochemical cycles are closely coupled, straw return may also affect soil reactive N (Nr) losses, but these effects remain uncertain, especially in terms of the interactions between soil C sequestration and Nr losses under straw addition. Here, we conducted a global meta-analysis using 363 publications to assess the overall effects of straw return on soil Nr losses, C sequestration and crop productivity in agroecosystems. Our results show that on average, compared to mineral N fertilization, straw return with same amount of mineral N fertilizer significantly increased soil organic C (SOC) content (14.9%), crop yield (5.1%), and crop N uptake (10.9%). Moreover, Nr losses in the form of nitrous oxide (N2O) emissions from rice paddies (17.3%), N leaching (8.7%), and runoff (25.6%) were significantly reduced, mainly due to enhanced microbial N immobilization. However, N2O emissions from upland fields (21.5%) and ammonia (NH3) emissions (17.0%) significantly increased following straw return, mainly due to the stimulation of nitrification/denitrification and soil urease activity. The increase in NH3 and N2O emissions was significantly and negatively correlated with straw C/N ratio and soil clay content. Regarding the interactions between C sequestration and Nr losses, the increase in SOC content following straw return was significantly and positively correlated with the decrease in N leaching and runoff. However, at a global scale, straw return increased net Nr losses from both rice and upland fields due to a greater stimulation of NH3 emissions than the reduction in N leaching and runoff. The trade-offs between increased net Nr losses and soil C sequestration highlight the importance of reasonably managing straw return to soils to limit NH3 emissions without decreasing associated C sequestration potential.
引用
收藏
页码:5919 / 5932
页数:14
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