Manuresheds: Advancing nutrient recycling in US agriculture
Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threat...
Ausführliche Beschreibung
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| Autor*in: |
Spiegal, Sheri [verfasserIn] Kleinman, Peter J.A. [verfasserIn] Endale, Dinku M. [verfasserIn] Bryant, Ray B. [verfasserIn] Dell, Curtis [verfasserIn] Goslee, Sarah [verfasserIn] Meinen, Robert J. [verfasserIn] Flynn, K. Colton [verfasserIn] Baker, John M. [verfasserIn] Browning, Dawn M. [verfasserIn] McCarty, Greg [verfasserIn] Bittman, Shabtai [verfasserIn] Carter, Jennifer [verfasserIn] Cavigelli, Michel [verfasserIn] Duncan, Emily [verfasserIn] Gowda, Prasanna [verfasserIn] Li, Xia [verfasserIn] Ponce-Campos, Guillermo E. [verfasserIn] Cibin, Raj [verfasserIn] Silveira, Maria L. [verfasserIn] Smith, Doulas R. [verfasserIn] Arthur, Dan K. [verfasserIn] Yang, Qichun [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2020 |
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| Schlagwörter: |
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| Übergeordnetes Werk: |
Enthalten in: Agricultural systems - Amsterdam [u.a.] : Elsevier, 1976, 182 |
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| Übergeordnetes Werk: |
volume:182 |
| DOI / URN: |
10.1016/j.agsy.2020.102813 |
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| Katalog-ID: |
ELV004131185 |
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| 520 | |a Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. | ||
| 650 | 4 | |a Livestock manure | |
| 650 | 4 | |a Nutrients | |
| 650 | 4 | |a Agriculture | |
| 650 | 4 | |a Phosphorus | |
| 650 | 4 | |a Nitrogen | |
| 650 | 4 | |a Long-Term Agroecosystem Research (LTAR) network | |
| 700 | 1 | |a Kleinman, Peter J.A. |e verfasserin |4 aut | |
| 700 | 1 | |a Endale, Dinku M. |e verfasserin |4 aut | |
| 700 | 1 | |a Bryant, Ray B. |e verfasserin |4 aut | |
| 700 | 1 | |a Dell, Curtis |e verfasserin |4 aut | |
| 700 | 1 | |a Goslee, Sarah |e verfasserin |4 aut | |
| 700 | 1 | |a Meinen, Robert J. |e verfasserin |4 aut | |
| 700 | 1 | |a Flynn, K. Colton |e verfasserin |4 aut | |
| 700 | 1 | |a Baker, John M. |e verfasserin |4 aut | |
| 700 | 1 | |a Browning, Dawn M. |e verfasserin |4 aut | |
| 700 | 1 | |a McCarty, Greg |e verfasserin |4 aut | |
| 700 | 1 | |a Bittman, Shabtai |e verfasserin |4 aut | |
| 700 | 1 | |a Carter, Jennifer |e verfasserin |4 aut | |
| 700 | 1 | |a Cavigelli, Michel |e verfasserin |4 aut | |
| 700 | 1 | |a Duncan, Emily |e verfasserin |4 aut | |
| 700 | 1 | |a Gowda, Prasanna |e verfasserin |4 aut | |
| 700 | 1 | |a Li, Xia |e verfasserin |4 aut | |
| 700 | 1 | |a Ponce-Campos, Guillermo E. |e verfasserin |4 aut | |
| 700 | 1 | |a Cibin, Raj |e verfasserin |4 aut | |
| 700 | 1 | |a Silveira, Maria L. |e verfasserin |4 aut | |
| 700 | 1 | |a Smith, Doulas R. |e verfasserin |4 aut | |
| 700 | 1 | |a Arthur, Dan K. |e verfasserin |4 aut | |
| 700 | 1 | |a Yang, Qichun |e verfasserin |4 aut | |
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10.1016/j.agsy.2020.102813 doi (DE-627)ELV004131185 (ELSEVIER)S0308-521X(19)31167-9 DE-627 ger DE-627 rda eng 630 640 DE-600 49.00 bkl 48.00 bkl Spiegal, Sheri verfasserin aut Manuresheds: Advancing nutrient recycling in US agriculture 2020 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. Livestock manure Nutrients Agriculture Phosphorus Nitrogen Long-Term Agroecosystem Research (LTAR) network Kleinman, Peter J.A. verfasserin aut Endale, Dinku M. verfasserin aut Bryant, Ray B. verfasserin aut Dell, Curtis verfasserin aut Goslee, Sarah verfasserin aut Meinen, Robert J. verfasserin aut Flynn, K. Colton verfasserin aut Baker, John M. verfasserin aut Browning, Dawn M. verfasserin aut McCarty, Greg verfasserin aut Bittman, Shabtai verfasserin aut Carter, Jennifer verfasserin aut Cavigelli, Michel verfasserin aut Duncan, Emily verfasserin aut Gowda, Prasanna verfasserin aut Li, Xia verfasserin aut Ponce-Campos, Guillermo E. verfasserin aut Cibin, Raj verfasserin aut Silveira, Maria L. verfasserin aut Smith, Doulas R. verfasserin aut Arthur, Dan K. verfasserin aut Yang, Qichun verfasserin aut Enthalten in Agricultural systems Amsterdam [u.a.] : Elsevier, 1976 182 Online-Ressource (DE-627)306311003 (DE-600)1495825-9 (DE-576)255637659 0308-521X nnns volume:182 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OPC-FOR GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 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_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 49.00 Hauswirtschaft: Allgemeines 48.00 Land- und Forstwirtschaft: Allgemeines AR 182 |
| spelling |
10.1016/j.agsy.2020.102813 doi (DE-627)ELV004131185 (ELSEVIER)S0308-521X(19)31167-9 DE-627 ger DE-627 rda eng 630 640 DE-600 49.00 bkl 48.00 bkl Spiegal, Sheri verfasserin aut Manuresheds: Advancing nutrient recycling in US agriculture 2020 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. Livestock manure Nutrients Agriculture Phosphorus Nitrogen Long-Term Agroecosystem Research (LTAR) network Kleinman, Peter J.A. verfasserin aut Endale, Dinku M. verfasserin aut Bryant, Ray B. verfasserin aut Dell, Curtis verfasserin aut Goslee, Sarah verfasserin aut Meinen, Robert J. verfasserin aut Flynn, K. Colton verfasserin aut Baker, John M. verfasserin aut Browning, Dawn M. verfasserin aut McCarty, Greg verfasserin aut Bittman, Shabtai verfasserin aut Carter, Jennifer verfasserin aut Cavigelli, Michel verfasserin aut Duncan, Emily verfasserin aut Gowda, Prasanna verfasserin aut Li, Xia verfasserin aut Ponce-Campos, Guillermo E. verfasserin aut Cibin, Raj verfasserin aut Silveira, Maria L. verfasserin aut Smith, Doulas R. verfasserin aut Arthur, Dan K. verfasserin aut Yang, Qichun verfasserin aut Enthalten in Agricultural systems Amsterdam [u.a.] : Elsevier, 1976 182 Online-Ressource (DE-627)306311003 (DE-600)1495825-9 (DE-576)255637659 0308-521X nnns volume:182 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OPC-FOR GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 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_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 49.00 Hauswirtschaft: Allgemeines 48.00 Land- und Forstwirtschaft: Allgemeines AR 182 |
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10.1016/j.agsy.2020.102813 doi (DE-627)ELV004131185 (ELSEVIER)S0308-521X(19)31167-9 DE-627 ger DE-627 rda eng 630 640 DE-600 49.00 bkl 48.00 bkl Spiegal, Sheri verfasserin aut Manuresheds: Advancing nutrient recycling in US agriculture 2020 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. Livestock manure Nutrients Agriculture Phosphorus Nitrogen Long-Term Agroecosystem Research (LTAR) network Kleinman, Peter J.A. verfasserin aut Endale, Dinku M. verfasserin aut Bryant, Ray B. verfasserin aut Dell, Curtis verfasserin aut Goslee, Sarah verfasserin aut Meinen, Robert J. verfasserin aut Flynn, K. Colton verfasserin aut Baker, John M. verfasserin aut Browning, Dawn M. verfasserin aut McCarty, Greg verfasserin aut Bittman, Shabtai verfasserin aut Carter, Jennifer verfasserin aut Cavigelli, Michel verfasserin aut Duncan, Emily verfasserin aut Gowda, Prasanna verfasserin aut Li, Xia verfasserin aut Ponce-Campos, Guillermo E. verfasserin aut Cibin, Raj verfasserin aut Silveira, Maria L. verfasserin aut Smith, Doulas R. verfasserin aut Arthur, Dan K. verfasserin aut Yang, Qichun verfasserin aut Enthalten in Agricultural systems Amsterdam [u.a.] : Elsevier, 1976 182 Online-Ressource (DE-627)306311003 (DE-600)1495825-9 (DE-576)255637659 0308-521X nnns volume:182 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OPC-FOR GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 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_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 49.00 Hauswirtschaft: Allgemeines 48.00 Land- und Forstwirtschaft: Allgemeines AR 182 |
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10.1016/j.agsy.2020.102813 doi (DE-627)ELV004131185 (ELSEVIER)S0308-521X(19)31167-9 DE-627 ger DE-627 rda eng 630 640 DE-600 49.00 bkl 48.00 bkl Spiegal, Sheri verfasserin aut Manuresheds: Advancing nutrient recycling in US agriculture 2020 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. Livestock manure Nutrients Agriculture Phosphorus Nitrogen Long-Term Agroecosystem Research (LTAR) network Kleinman, Peter J.A. verfasserin aut Endale, Dinku M. verfasserin aut Bryant, Ray B. verfasserin aut Dell, Curtis verfasserin aut Goslee, Sarah verfasserin aut Meinen, Robert J. verfasserin aut Flynn, K. Colton verfasserin aut Baker, John M. verfasserin aut Browning, Dawn M. verfasserin aut McCarty, Greg verfasserin aut Bittman, Shabtai verfasserin aut Carter, Jennifer verfasserin aut Cavigelli, Michel verfasserin aut Duncan, Emily verfasserin aut Gowda, Prasanna verfasserin aut Li, Xia verfasserin aut Ponce-Campos, Guillermo E. verfasserin aut Cibin, Raj verfasserin aut Silveira, Maria L. verfasserin aut Smith, Doulas R. verfasserin aut Arthur, Dan K. verfasserin aut Yang, Qichun verfasserin aut Enthalten in Agricultural systems Amsterdam [u.a.] : Elsevier, 1976 182 Online-Ressource (DE-627)306311003 (DE-600)1495825-9 (DE-576)255637659 0308-521X nnns volume:182 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OPC-FOR GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 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_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 49.00 Hauswirtschaft: Allgemeines 48.00 Land- und Forstwirtschaft: Allgemeines AR 182 |
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10.1016/j.agsy.2020.102813 doi (DE-627)ELV004131185 (ELSEVIER)S0308-521X(19)31167-9 DE-627 ger DE-627 rda eng 630 640 DE-600 49.00 bkl 48.00 bkl Spiegal, Sheri verfasserin aut Manuresheds: Advancing nutrient recycling in US agriculture 2020 nicht spezifiziert zzz rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. Livestock manure Nutrients Agriculture Phosphorus Nitrogen Long-Term Agroecosystem Research (LTAR) network Kleinman, Peter J.A. verfasserin aut Endale, Dinku M. verfasserin aut Bryant, Ray B. verfasserin aut Dell, Curtis verfasserin aut Goslee, Sarah verfasserin aut Meinen, Robert J. verfasserin aut Flynn, K. Colton verfasserin aut Baker, John M. verfasserin aut Browning, Dawn M. verfasserin aut McCarty, Greg verfasserin aut Bittman, Shabtai verfasserin aut Carter, Jennifer verfasserin aut Cavigelli, Michel verfasserin aut Duncan, Emily verfasserin aut Gowda, Prasanna verfasserin aut Li, Xia verfasserin aut Ponce-Campos, Guillermo E. verfasserin aut Cibin, Raj verfasserin aut Silveira, Maria L. verfasserin aut Smith, Doulas R. verfasserin aut Arthur, Dan K. verfasserin aut Yang, Qichun verfasserin aut Enthalten in Agricultural systems Amsterdam [u.a.] : Elsevier, 1976 182 Online-Ressource (DE-627)306311003 (DE-600)1495825-9 (DE-576)255637659 0308-521X nnns volume:182 GBV_USEFLAG_U SYSFLAG_U GBV_ELV SSG-OPC-FOR GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 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_151 GBV_ILN_224 GBV_ILN_370 GBV_ILN_602 GBV_ILN_702 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2027 GBV_ILN_2034 GBV_ILN_2038 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2056 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2190 GBV_ILN_2336 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4313 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4325 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4338 GBV_ILN_4393 49.00 Hauswirtschaft: Allgemeines 48.00 Land- und Forstwirtschaft: Allgemeines AR 182 |
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As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. 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Spiegal, Sheri |
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Spiegal, Sheri ddc 630 bkl 49.00 bkl 48.00 misc Livestock manure misc Nutrients misc Agriculture misc Phosphorus misc Nitrogen misc Long-Term Agroecosystem Research (LTAR) network Manuresheds: Advancing nutrient recycling in US agriculture |
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Spiegal, Sheri Kleinman, Peter J.A. Endale, Dinku M. Bryant, Ray B. Dell, Curtis Goslee, Sarah Meinen, Robert J. Flynn, K. Colton Baker, John M. Browning, Dawn M. McCarty, Greg Bittman, Shabtai Carter, Jennifer Cavigelli, Michel Duncan, Emily Gowda, Prasanna Li, Xia Ponce-Campos, Guillermo E. Cibin, Raj Silveira, Maria L. Smith, Doulas R. Arthur, Dan K. Yang, Qichun |
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manuresheds: advancing nutrient recycling in us agriculture |
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Manuresheds: Advancing nutrient recycling in US agriculture |
| abstract |
Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. |
| abstractGer |
Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. |
| abstract_unstemmed |
Nutrient recycling is fundamental to sustainable agricultural systems, but few mechanisms exist to ensure that surplus manure nutrients from animal feeding operations are transported for use on nutrient-deficient croplands. As a result, manure nutrients concentrate in locations where they can threaten environmental health and devalue manure as a fertilizer resource. This study advances the concept of the “manureshed” – the lands surrounding animal feeding operations onto which manure nutrients can be redistributed to meet environmental, production, and economic goals. Manuresheds can be managed at multiple scales, for example, on farms with both animals and crops, among animal farms and crop farms within a county, or even among animal farms and crop farms in distant counties. With a focus on redistribution among counties, we classified the 3109 counties of the contiguous United States by their capacity to either supply manure phosphorus (P) and nitrogen (N) from confined livestock production (“sources”) or to assimilate and remove excess P and N via crops (“sinks”). Manure nutrient source counties were identified in 40 of the 48 states, with a substantial concentration in the southern US. Source counties for manure P greatly outnumbered source counties for manure N (390 vs. 100), and 99 of the 100 manure N source counties were also source counties for manure P. Conversely, sink counties for manure N outnumbered sink counties for manure P (2766 vs. 2317). We used the P balances of the source and sink counties to delineate four manuresheds dominated by various combinations of confined hog, poultry, dairy, and beef industries. The four manuresheds differed in the transport distances needed to assimilate excess manure P from their respective source areas (from 147 ± 51 km for a beef dominated manureshed to 368 ± 140 km for a poultry dominated manureshed), highlighting the need for systems-level strategies to promote manure nutrient recycling that operate across local, county, regional, and national scales. |
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| title_short |
Manuresheds: Advancing nutrient recycling in US agriculture |
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| author2 |
Kleinman, Peter J.A. Endale, Dinku M. Bryant, Ray B. Dell, Curtis Goslee, Sarah Meinen, Robert J. Flynn, K. Colton Baker, John M. Browning, Dawn M. McCarty, Greg Bittman, Shabtai Carter, Jennifer Cavigelli, Michel Duncan, Emily Gowda, Prasanna Li, Xia Ponce-Campos, Guillermo E. Cibin, Raj Silveira, Maria L. Smith, Doulas R. Arthur, Dan K. Yang, Qichun |
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Kleinman, Peter J.A. Endale, Dinku M. Bryant, Ray B. Dell, Curtis Goslee, Sarah Meinen, Robert J. Flynn, K. Colton Baker, John M. Browning, Dawn M. McCarty, Greg Bittman, Shabtai Carter, Jennifer Cavigelli, Michel Duncan, Emily Gowda, Prasanna Li, Xia Ponce-Campos, Guillermo E. Cibin, Raj Silveira, Maria L. Smith, Doulas R. Arthur, Dan K. Yang, Qichun |
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| doi_str |
10.1016/j.agsy.2020.102813 |
| up_date |
2024-07-06T21:57:19.386Z |
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