Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil
Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive produ...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Kayser, Manfred [verfasserIn] Benke, Matthias [verfasserIn] Isselstein, Johannes [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2011 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Agronomy for sustainable development - Berlin : Springer, 1981, 31(2011), 4 vom: 04. Aug. |
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| Übergeordnetes Werk: |
volume:31 ; year:2011 ; number:4 ; day:04 ; month:08 |
| Links: |
|---|
| DOI / URN: |
10.1007/s13593-011-0046-9 |
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| Katalog-ID: |
SPR031882552 |
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| 245 | 1 | 0 | |a Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil |
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| 520 | |a Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. | ||
| 650 | 4 | |a Maize |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Nitrogen losses |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Manure |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Leaching |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Organic matter |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Mineralization |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Benke, Matthias |e verfasserin |4 aut | |
| 700 | 1 | |a Isselstein, Johannes |e verfasserin |4 aut | |
| 773 | 0 | 8 | |i Enthalten in |t Agronomy for sustainable development |d Berlin : Springer, 1981 |g 31(2011), 4 vom: 04. Aug. |w (DE-627)312838921 |w (DE-600)2012314-0 |x 1773-0155 |7 nnns |
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2011 |
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2011 |
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10.1007/s13593-011-0046-9 doi (DE-627)SPR031882552 (SPR)s13593-011-0046-9-e DE-627 ger DE-627 rakwb eng 580 630 640 ASE 48.16 bkl Kayser, Manfred verfasserin aut Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. Maize (dpeaa)DE-He213 Nitrogen losses (dpeaa)DE-He213 Manure (dpeaa)DE-He213 Leaching (dpeaa)DE-He213 Organic matter (dpeaa)DE-He213 Mineralization (dpeaa)DE-He213 Benke, Matthias verfasserin aut Isselstein, Johannes verfasserin aut Enthalten in Agronomy for sustainable development Berlin : Springer, 1981 31(2011), 4 vom: 04. Aug. (DE-627)312838921 (DE-600)2012314-0 1773-0155 nnns volume:31 year:2011 number:4 day:04 month:08 https://dx.doi.org/10.1007/s13593-011-0046-9 kostenfrei 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_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.16 ASE AR 31 2011 4 04 08 |
| spelling |
10.1007/s13593-011-0046-9 doi (DE-627)SPR031882552 (SPR)s13593-011-0046-9-e DE-627 ger DE-627 rakwb eng 580 630 640 ASE 48.16 bkl Kayser, Manfred verfasserin aut Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. Maize (dpeaa)DE-He213 Nitrogen losses (dpeaa)DE-He213 Manure (dpeaa)DE-He213 Leaching (dpeaa)DE-He213 Organic matter (dpeaa)DE-He213 Mineralization (dpeaa)DE-He213 Benke, Matthias verfasserin aut Isselstein, Johannes verfasserin aut Enthalten in Agronomy for sustainable development Berlin : Springer, 1981 31(2011), 4 vom: 04. Aug. (DE-627)312838921 (DE-600)2012314-0 1773-0155 nnns volume:31 year:2011 number:4 day:04 month:08 https://dx.doi.org/10.1007/s13593-011-0046-9 kostenfrei 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_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.16 ASE AR 31 2011 4 04 08 |
| allfields_unstemmed |
10.1007/s13593-011-0046-9 doi (DE-627)SPR031882552 (SPR)s13593-011-0046-9-e DE-627 ger DE-627 rakwb eng 580 630 640 ASE 48.16 bkl Kayser, Manfred verfasserin aut Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. Maize (dpeaa)DE-He213 Nitrogen losses (dpeaa)DE-He213 Manure (dpeaa)DE-He213 Leaching (dpeaa)DE-He213 Organic matter (dpeaa)DE-He213 Mineralization (dpeaa)DE-He213 Benke, Matthias verfasserin aut Isselstein, Johannes verfasserin aut Enthalten in Agronomy for sustainable development Berlin : Springer, 1981 31(2011), 4 vom: 04. Aug. (DE-627)312838921 (DE-600)2012314-0 1773-0155 nnns volume:31 year:2011 number:4 day:04 month:08 https://dx.doi.org/10.1007/s13593-011-0046-9 kostenfrei 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_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.16 ASE AR 31 2011 4 04 08 |
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10.1007/s13593-011-0046-9 doi (DE-627)SPR031882552 (SPR)s13593-011-0046-9-e DE-627 ger DE-627 rakwb eng 580 630 640 ASE 48.16 bkl Kayser, Manfred verfasserin aut Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. Maize (dpeaa)DE-He213 Nitrogen losses (dpeaa)DE-He213 Manure (dpeaa)DE-He213 Leaching (dpeaa)DE-He213 Organic matter (dpeaa)DE-He213 Mineralization (dpeaa)DE-He213 Benke, Matthias verfasserin aut Isselstein, Johannes verfasserin aut Enthalten in Agronomy for sustainable development Berlin : Springer, 1981 31(2011), 4 vom: 04. Aug. (DE-627)312838921 (DE-600)2012314-0 1773-0155 nnns volume:31 year:2011 number:4 day:04 month:08 https://dx.doi.org/10.1007/s13593-011-0046-9 kostenfrei 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_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.16 ASE AR 31 2011 4 04 08 |
| allfieldsSound |
10.1007/s13593-011-0046-9 doi (DE-627)SPR031882552 (SPR)s13593-011-0046-9-e DE-627 ger DE-627 rakwb eng 580 630 640 ASE 48.16 bkl Kayser, Manfred verfasserin aut Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil 2011 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. Maize (dpeaa)DE-He213 Nitrogen losses (dpeaa)DE-He213 Manure (dpeaa)DE-He213 Leaching (dpeaa)DE-He213 Organic matter (dpeaa)DE-He213 Mineralization (dpeaa)DE-He213 Benke, Matthias verfasserin aut Isselstein, Johannes verfasserin aut Enthalten in Agronomy for sustainable development Berlin : Springer, 1981 31(2011), 4 vom: 04. Aug. (DE-627)312838921 (DE-600)2012314-0 1773-0155 nnns volume:31 year:2011 number:4 day:04 month:08 https://dx.doi.org/10.1007/s13593-011-0046-9 kostenfrei 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_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_161 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 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_2116 GBV_ILN_2118 GBV_ILN_2119 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_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 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_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 48.16 ASE AR 31 2011 4 04 08 |
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English |
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Enthalten in Agronomy for sustainable development 31(2011), 4 vom: 04. Aug. volume:31 year:2011 number:4 day:04 month:08 |
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Maize Nitrogen losses Manure Leaching Organic matter Mineralization |
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Agronomy for sustainable development |
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Kayser, Manfred @@aut@@ Benke, Matthias @@aut@@ Isselstein, Johannes @@aut@@ |
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Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. 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| author |
Kayser, Manfred |
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Kayser, Manfred ddc 580 bkl 48.16 misc Maize misc Nitrogen losses misc Manure misc Leaching misc Organic matter misc Mineralization Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil |
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580 630 640 ASE 48.16 bkl Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil Maize (dpeaa)DE-He213 Nitrogen losses (dpeaa)DE-He213 Manure (dpeaa)DE-He213 Leaching (dpeaa)DE-He213 Organic matter (dpeaa)DE-He213 Mineralization (dpeaa)DE-He213 |
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ddc 580 bkl 48.16 misc Maize misc Nitrogen losses misc Manure misc Leaching misc Organic matter misc Mineralization |
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ddc 580 bkl 48.16 misc Maize misc Nitrogen losses misc Manure misc Leaching misc Organic matter misc Mineralization |
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Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil |
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Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil |
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Kayser, Manfred |
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Agronomy for sustainable development |
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little fertilizer response but high n loss risk of maize on a productive organic-sandy soil |
| title_auth |
Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil |
| abstract |
Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. |
| abstractGer |
Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. |
| abstract_unstemmed |
Abstract Information on the environmental impact of maize production is actually inconsistent. Indeed some experiments report good nitrogen (N) efficiencies and small residual N. Other experiments show large leaching losses, while in practice maize production is often coupled with an intensive production and large N surpluses. Here, we present data from a 4-year experiment with silage maize on a sandy soil of high mineralization potential. The experimental set-up included three N input forms, mineral, cattle and pig slurry and four rates of total N, of 0, 80, 160 and 240 kg N $ ha^{−1} $ $ year^{−1} $ and the use of suction cups. Results show that dry matter and N yields for N0–N240 were relatively high and consistent (158–192 kg N $ ha^{−1} $). Further findings show large residual soil mineral nitrogen, of 138–237 kg N $ ha^{−1} $, and high nitrate concentrations in leaching water during winter, of 39–73 mg $ NO_{3} $–N $ L^{−1} $, corresponding to leaching losses of 86–152 kg N $ ha^{−1} $. Response to N input was small with apparent N recoveries of 14–22% for manures and mineral fertilizers. We conclude that caution is needed when maize production is extended to fields with an apparently high potential for mineralization and that use as grassland would be a better alternative with regard to N leaching losses. |
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4 |
| title_short |
Little fertilizer response but high N loss risk of maize on a productive organic-sandy soil |
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https://dx.doi.org/10.1007/s13593-011-0046-9 |
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| author2 |
Benke, Matthias Isselstein, Johannes |
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Benke, Matthias Isselstein, Johannes |
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| doi_str |
10.1007/s13593-011-0046-9 |
| up_date |
2024-07-04T01:39:33.740Z |
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1803610671014739968 |
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| score |
7.397339 |