| 000 | 02960nab a22004217a 4500 | ||
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| 999 |
_c61408 _d61400 |
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| 001 | 61408 | ||
| 003 | MX-TxCIM | ||
| 005 | 20240919020917.0 | ||
| 008 | 200221s2020 xxk|||p|op||| 00| 0 eng d | ||
| 022 | _a0365-0340 | ||
| 022 | _a1476-3567 (Online) | ||
| 024 | 8 | _ahttps://doi.org/10.1080/03650340.2019.1708332 | |
| 040 | _aMX-TxCIM | ||
| 041 | _aeng | ||
| 100 | 1 |
_aSapkota, T.B. _gSustainable Intensification Program _gSustainable Agrifood Systems _8INT3361 _9940 |
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| 245 | 1 | 0 | _aIdentifying optimum rates of fertilizer nitrogen application to maximize economic return and minimize nitrous oxide emission from rice–wheat systems in the Indo-Gangetic Plains of India |
| 260 |
_aUnited Kingdom : _bTaylor & Francis, _c2020. |
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| 500 | _aPeer review | ||
| 500 | _aOpen Access | ||
| 520 | _aRice–wheat (RW) cropping system in India is a major source of N2O emissions. In such system, defining N rates that deliver minimal N2O emissions and economically optimum yield would benefit both food production and the environment. We measured yield and N2O fluxes from RW systems in Northwest IGP under two tillage systems and five N rates (0, 75, 150, 225 and 300 kg N ha−1) for both rice and wheat using static chamber method. Seasonal pattern of N2O emission was mainly influenced by fertilizer and water application events with no significant effect of tillage systems. Mean annual N2O emission from RW system was 1.49 kg N ha−1 in N75 plot and 2.97–3.04 in the plots receiving ≥150 kg N ha−1. On average, the yield-scaled N2O emissions of rice and wheat were 0.25 and 0.52 kg N2O–N mg−1, respectively. Our finding suggests that N rates between 120–200 kg N ha−1 in rice and 50–185 kg ha−1 in wheat provide the most economical returns and application rates beyond these ranges would be both economically and environmentally unsustainable. Within the range of N rate studied, fertilizer-induced N2O-EF for rice and wheat were 0.41% and 0.79%, respectively. | ||
| 526 | _aCCAFS | ||
| 546 | _aText in English | ||
| 650 | 7 |
_2AGROVOC _94669 _aNitrous oxide |
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| 650 | 7 |
_2AGROVOC _911417 _aEmission |
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| 650 | 7 |
_2AGROVOC _98210 _aGreenhouse gas emissions |
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| 650 | 7 |
_aCropping systems _gAGROVOC _2 _91068 |
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| 651 | 7 |
_2AGROVOC _93726 _aIndia |
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| 700 | 1 |
_91492 _aSingh, L.K. |
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| 700 | 1 |
_95698 _aYadav, A.K. |
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| 700 | 1 |
_8I1706974 _91402 _aKhatri-Chhetri, A. _gBorlaug Institute of South Asia |
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| 700 | 1 |
_95697 _aJat, H.S. |
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| 700 | 1 |
_92439 _aSharma, P.C. |
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| 700 | 1 |
_aJat, M.L. _gFormerly Sustainable Intensification Program _gFormerly Sustainable Agrifood Systems _8INT3072 _9889 |
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| 700 | 1 |
_8INT3349 _9930 _aStirling, C. _gSustainable Intensification Program |
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| 773 | 0 |
_dUnited Kingdom : Taylor & Francis, 2020. _gv. 66, no. 14, p. 2039-2054 _tArchives of Agronomy and Soil Science _w94785 _x0365-0340 |
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| 856 | 4 |
_yOpen Access through DSpace _uhttps://hdl.handle.net/10883/20782 |
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| 942 |
_2ddc _cJA _n0 |
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