Nitrous oxide emissions from manured, no-till corn systems

Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior l...
Ausführliche Beschreibung

Gespeichert in:

Autor*in:	Ponce de León, María A. [verfasserIn] Dell, Curtis J. [verfasserIn] Karsten, Heather D. [verfasserIn]

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2021

Schlagwörter:	Crop residue Crop rotations Dairy manure Inorganic fertilizer Manure injection Nitrous oxide emissions

Übergeordnetes Werk:	Enthalten in: Nutrient cycling in agroecosystems - Dordrecht [u.a.] : Springer Science + Business Media B.V, 1980, 119(2021), 3 vom: 26. März, Seite 405-421
Übergeordnetes Werk:	volume:119 ; year:2021 ; number:3 ; day:26 ; month:03 ; pages:405-421

Links:	Volltext

DOI / URN:	10.1007/s10705-021-10131-y

Katalog-ID:	SPR043736734

Internformat


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100	1		\|a Ponce de León, María A. \|e verfasserin \|4 aut
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520			\|a Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification.
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650		4	\|a Manure injection \|7 (dpeaa)DE-He213
650		4	\|a Nitrous oxide emissions \|7 (dpeaa)DE-He213
700	1		\|a Dell, Curtis J. \|e verfasserin \|4 aut
700	1		\|a Karsten, Heather D. \|e verfasserin \|4 aut
773	0	8	\|i Enthalten in \|t Nutrient cycling in agroecosystems \|d Dordrecht [u.a.] : Springer Science + Business Media B.V, 1980 \|g 119(2021), 3 vom: 26. März, Seite 405-421 \|w (DE-627)270932712 \|w (DE-600)1478384-8 \|x 1573-0867 \|7 nnns
773	1	8	\|g volume:119 \|g year:2021 \|g number:3 \|g day:26 \|g month:03 \|g pages:405-421
856	4	0	\|u https://dx.doi.org/10.1007/s10705-021-10131-y \|z lizenzpflichtig \|3 Volltext
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912			\|a GBV_ILN_40
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912			\|a GBV_ILN_62
912			\|a GBV_ILN_63
912			\|a GBV_ILN_65
912			\|a GBV_ILN_69
912			\|a GBV_ILN_70
912			\|a GBV_ILN_73
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912			\|a GBV_ILN_90
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912			\|a GBV_ILN_100
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912			\|a GBV_ILN_105
912			\|a GBV_ILN_110
912			\|a GBV_ILN_120
912			\|a GBV_ILN_138
912			\|a GBV_ILN_150
912			\|a GBV_ILN_151
912			\|a GBV_ILN_152
912			\|a GBV_ILN_161
912			\|a GBV_ILN_170
912			\|a GBV_ILN_171
912			\|a GBV_ILN_187
912			\|a GBV_ILN_213
912			\|a GBV_ILN_224
912			\|a GBV_ILN_230
912			\|a GBV_ILN_250
912			\|a GBV_ILN_281
912			\|a GBV_ILN_285
912			\|a GBV_ILN_293
912			\|a GBV_ILN_370
912			\|a GBV_ILN_602
912			\|a GBV_ILN_636
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2001
912			\|a GBV_ILN_2003
912			\|a GBV_ILN_2004
912			\|a GBV_ILN_2005
912			\|a GBV_ILN_2006
912			\|a GBV_ILN_2007
912			\|a GBV_ILN_2008
912			\|a GBV_ILN_2009
912			\|a GBV_ILN_2010
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912			\|a GBV_ILN_2015
912			\|a GBV_ILN_2020
912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
912			\|a GBV_ILN_2026
912			\|a GBV_ILN_2027
912			\|a GBV_ILN_2031
912			\|a GBV_ILN_2034
912			\|a GBV_ILN_2037
912			\|a GBV_ILN_2038
912			\|a GBV_ILN_2039
912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
912			\|a GBV_ILN_2055
912			\|a GBV_ILN_2056
912			\|a GBV_ILN_2057
912			\|a GBV_ILN_2059
912			\|a GBV_ILN_2061
912			\|a GBV_ILN_2064
912			\|a GBV_ILN_2065
912			\|a GBV_ILN_2068
912			\|a GBV_ILN_2088
912			\|a GBV_ILN_2093
912			\|a GBV_ILN_2106
912			\|a GBV_ILN_2107
912			\|a GBV_ILN_2108
912			\|a GBV_ILN_2110
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912			\|a GBV_ILN_4322
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912			\|a GBV_ILN_4326
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912			\|a GBV_ILN_4333
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912			\|a GBV_ILN_4335
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Indexfelder

author_variant	d l m a p dlma dlmap c j d cj cjd h d k hd hdk
matchkey_str	article:15730867:2021----::iruoiemsinfomnrdoi
hierarchy_sort_str	2021
bklnumber	48.52 48.16
publishDate	2021
allfields	10.1007/s10705-021-10131-y doi (DE-627)SPR043736734 (DE-599)SPRs10705-021-10131-y-e (SPR)s10705-021-10131-y-e DE-627 ger DE-627 rakwb eng 570 ASE 48.52 bkl 48.16 bkl Ponce de León, María A. verfasserin aut Nitrous oxide emissions from manured, no-till corn systems 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification. Crop residue (dpeaa)DE-He213 Crop rotations (dpeaa)DE-He213 Dairy manure (dpeaa)DE-He213 Inorganic fertilizer (dpeaa)DE-He213 Manure injection (dpeaa)DE-He213 Nitrous oxide emissions (dpeaa)DE-He213 Dell, Curtis J. verfasserin aut Karsten, Heather D. verfasserin aut Enthalten in Nutrient cycling in agroecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1980 119(2021), 3 vom: 26. März, Seite 405-421 (DE-627)270932712 (DE-600)1478384-8 1573-0867 nnns volume:119 year:2021 number:3 day:26 month:03 pages:405-421 https://dx.doi.org/10.1007/s10705-021-10131-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.52 ASE 48.16 ASE AR 119 2021 3 26 03 405-421
spelling	10.1007/s10705-021-10131-y doi (DE-627)SPR043736734 (DE-599)SPRs10705-021-10131-y-e (SPR)s10705-021-10131-y-e DE-627 ger DE-627 rakwb eng 570 ASE 48.52 bkl 48.16 bkl Ponce de León, María A. verfasserin aut Nitrous oxide emissions from manured, no-till corn systems 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification. Crop residue (dpeaa)DE-He213 Crop rotations (dpeaa)DE-He213 Dairy manure (dpeaa)DE-He213 Inorganic fertilizer (dpeaa)DE-He213 Manure injection (dpeaa)DE-He213 Nitrous oxide emissions (dpeaa)DE-He213 Dell, Curtis J. verfasserin aut Karsten, Heather D. verfasserin aut Enthalten in Nutrient cycling in agroecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1980 119(2021), 3 vom: 26. März, Seite 405-421 (DE-627)270932712 (DE-600)1478384-8 1573-0867 nnns volume:119 year:2021 number:3 day:26 month:03 pages:405-421 https://dx.doi.org/10.1007/s10705-021-10131-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.52 ASE 48.16 ASE AR 119 2021 3 26 03 405-421
allfields_unstemmed	10.1007/s10705-021-10131-y doi (DE-627)SPR043736734 (DE-599)SPRs10705-021-10131-y-e (SPR)s10705-021-10131-y-e DE-627 ger DE-627 rakwb eng 570 ASE 48.52 bkl 48.16 bkl Ponce de León, María A. verfasserin aut Nitrous oxide emissions from manured, no-till corn systems 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification. Crop residue (dpeaa)DE-He213 Crop rotations (dpeaa)DE-He213 Dairy manure (dpeaa)DE-He213 Inorganic fertilizer (dpeaa)DE-He213 Manure injection (dpeaa)DE-He213 Nitrous oxide emissions (dpeaa)DE-He213 Dell, Curtis J. verfasserin aut Karsten, Heather D. verfasserin aut Enthalten in Nutrient cycling in agroecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1980 119(2021), 3 vom: 26. März, Seite 405-421 (DE-627)270932712 (DE-600)1478384-8 1573-0867 nnns volume:119 year:2021 number:3 day:26 month:03 pages:405-421 https://dx.doi.org/10.1007/s10705-021-10131-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.52 ASE 48.16 ASE AR 119 2021 3 26 03 405-421
allfieldsGer	10.1007/s10705-021-10131-y doi (DE-627)SPR043736734 (DE-599)SPRs10705-021-10131-y-e (SPR)s10705-021-10131-y-e DE-627 ger DE-627 rakwb eng 570 ASE 48.52 bkl 48.16 bkl Ponce de León, María A. verfasserin aut Nitrous oxide emissions from manured, no-till corn systems 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification. Crop residue (dpeaa)DE-He213 Crop rotations (dpeaa)DE-He213 Dairy manure (dpeaa)DE-He213 Inorganic fertilizer (dpeaa)DE-He213 Manure injection (dpeaa)DE-He213 Nitrous oxide emissions (dpeaa)DE-He213 Dell, Curtis J. verfasserin aut Karsten, Heather D. verfasserin aut Enthalten in Nutrient cycling in agroecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1980 119(2021), 3 vom: 26. März, Seite 405-421 (DE-627)270932712 (DE-600)1478384-8 1573-0867 nnns volume:119 year:2021 number:3 day:26 month:03 pages:405-421 https://dx.doi.org/10.1007/s10705-021-10131-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.52 ASE 48.16 ASE AR 119 2021 3 26 03 405-421
allfieldsSound	10.1007/s10705-021-10131-y doi (DE-627)SPR043736734 (DE-599)SPRs10705-021-10131-y-e (SPR)s10705-021-10131-y-e DE-627 ger DE-627 rakwb eng 570 ASE 48.52 bkl 48.16 bkl Ponce de León, María A. verfasserin aut Nitrous oxide emissions from manured, no-till corn systems 2021 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification. Crop residue (dpeaa)DE-He213 Crop rotations (dpeaa)DE-He213 Dairy manure (dpeaa)DE-He213 Inorganic fertilizer (dpeaa)DE-He213 Manure injection (dpeaa)DE-He213 Nitrous oxide emissions (dpeaa)DE-He213 Dell, Curtis J. verfasserin aut Karsten, Heather D. verfasserin aut Enthalten in Nutrient cycling in agroecosystems Dordrecht [u.a.] : Springer Science + Business Media B.V, 1980 119(2021), 3 vom: 26. März, Seite 405-421 (DE-627)270932712 (DE-600)1478384-8 1573-0867 nnns volume:119 year:2021 number:3 day:26 month:03 pages:405-421 https://dx.doi.org/10.1007/s10705-021-10131-y lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4328 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.52 ASE 48.16 ASE AR 119 2021 3 26 03 405-421
language	English
source	Enthalten in Nutrient cycling in agroecosystems 119(2021), 3 vom: 26. März, Seite 405-421 volume:119 year:2021 number:3 day:26 month:03 pages:405-421
sourceStr	Enthalten in Nutrient cycling in agroecosystems 119(2021), 3 vom: 26. März, Seite 405-421 volume:119 year:2021 number:3 day:26 month:03 pages:405-421
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Crop residue Crop rotations Dairy manure Inorganic fertilizer Manure injection Nitrous oxide emissions
dewey-raw	570
isfreeaccess_bool	false
container_title	Nutrient cycling in agroecosystems
authorswithroles_txt_mv	Ponce de León, María A. @@aut@@ Dell, Curtis J. @@aut@@ Karsten, Heather D. @@aut@@
publishDateDaySort_date	2021-03-26T00:00:00Z
hierarchy_top_id	270932712
dewey-sort	3570
id	SPR043736734
language_de	englisch
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author	Ponce de León, María A.
spellingShingle	Ponce de León, María A. ddc 570 bkl 48.52 bkl 48.16 misc Crop residue misc Crop rotations misc Dairy manure misc Inorganic fertilizer misc Manure injection misc Nitrous oxide emissions Nitrous oxide emissions from manured, no-till corn systems
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topic_title	570 ASE 48.52 bkl 48.16 bkl Nitrous oxide emissions from manured, no-till corn systems Crop residue (dpeaa)DE-He213 Crop rotations (dpeaa)DE-He213 Dairy manure (dpeaa)DE-He213 Inorganic fertilizer (dpeaa)DE-He213 Manure injection (dpeaa)DE-He213 Nitrous oxide emissions (dpeaa)DE-He213
topic	ddc 570 bkl 48.52 bkl 48.16 misc Crop residue misc Crop rotations misc Dairy manure misc Inorganic fertilizer misc Manure injection misc Nitrous oxide emissions
topic_unstemmed	ddc 570 bkl 48.52 bkl 48.16 misc Crop residue misc Crop rotations misc Dairy manure misc Inorganic fertilizer misc Manure injection misc Nitrous oxide emissions
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title	Nitrous oxide emissions from manured, no-till corn systems
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title_full	Nitrous oxide emissions from manured, no-till corn systems
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author_browse	Ponce de León, María A. Dell, Curtis J. Karsten, Heather D.
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title_sort	nitrous oxide emissions from manured, no-till corn systems
title_auth	Nitrous oxide emissions from manured, no-till corn systems
abstract	Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification.
abstractGer	Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification.
abstract_unstemmed	Abstract Using dairy manure and legumes in crop rotations can reduce inorganic N inputs for corn (Zea mays L.), yet these practices can also contribute to nitrous oxide ($ N_{2} $O) emissions. In two crop rotations we investigated how different (i) organic and inorganic N amendments and (ii) prior legume crops with broadcast manure influenced direct $ N_{2} $O emissions from silt-loam soils planted to no-till corn. We measured $ N_{2} $O fluxes from April to December for two years using closed vented chambers from soils planted to corn with no spring residue to compare inorganic N fertilizer (S-UAN) and two liquid dairy manure application methods: surface broadcasted (S-BM) and injected (S-IM). Emissions were also measured to compare the effect of crop residue of perennial forages, a green manure legume, or soybean (Glycine max L. Merr.) from soils all amended with liquid dairy manure. Nitrous oxide emissions were greatest during the 15–45 days after manure was injected compared to broadcasting, and cumulative $ N_{2} $O emissions were larger from S-IM (2.8–2.5 kg $ ha^{−1} $) than S-BM (1.4–0.7 kg $ ha^{−1} $) and S-UAN (0.3 kg $ ha^{−1} $). Cumulative and yield-scaled $ N_{2} $O emissions did not differ among the prior legume treatments. A ranking approach based on random forests, identified the most important variable contributing to $ N_{2} $O emissions in both comparisons as corn growing degree days, indicative of the asynchrony of spring legume termination and manure application with corn planting and N use; and changing environmental conditions for N mineralization and denitrification.
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container_issue	3
title_short	Nitrous oxide emissions from manured, no-till corn systems
url	https://dx.doi.org/10.1007/s10705-021-10131-y
remote_bool	true
author2	Dell, Curtis J. Karsten, Heather D.
author2Str	Dell, Curtis J. Karsten, Heather D.
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doi_str	10.1007/s10705-021-10131-y
up_date	2024-07-03T20:33:08.636Z
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Nitrous oxide emissions from manured, no-till corn systems

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