TY - JOUR
T1 - Manuresheds
T2 - Advancing nutrient recycling in US agriculture
AU - Spiegal, Sheri
AU - Kleinman, Peter J.A.
AU - Endale, Dinku M.
AU - Bryant, Ray B.
AU - Dell, Curtis
AU - Goslee, Sarah
AU - Meinen, Robert J.
AU - Flynn, K. Colton
AU - Baker, John M.
AU - Browning, Dawn M.
AU - McCarty, Greg
AU - Bittman, Shabtai
AU - Carter, Jennifer
AU - Cavigelli, Michel
AU - Duncan, Emily
AU - Gowda, Prasanna
AU - Li, Xia
AU - Ponce-Campos, Guillermo E.
AU - Cibin, Raj
AU - Silveira, Maria L.
AU - Smith, Doulas R.
AU - Arthur, Dan K.
AU - Yang, Qichun
N1 - Funding Information:
This research was a contribution from the Long-Term Agroecosystem Research (LTAR) network. LTAR is supported by the United States Department of Agriculture. We thank Heidi Peterson and Tom Bruulsema of the International Plant Nutrition Institute for sharing their expertise about NuGIS. Thanks also to Mark Kautz of the LTAR Communications Working Group for graphic design of Fig. 1c, and to Bruce Vandenberg of the USDA Data Innovations Team for preparing and presenting our data products in the USDA Agricultural Collaborative Research Outcomes System (AgCROS). Thanks to two peer reviewers whose insightful and constructive comments helped to improve this work, and to Jeffrey E. Herrick, Brandon T. Bestelmeyer, Joel R. Brown, Peter Vadas, and Paul L. Spiegal for their helpful input. We are grateful to Noel Gollehon for his encouragement and guidance at the start of the LTAR Manureshed Project.
Funding Information:
This research was a contribution from the Long-Term Agroecosystem Research (LTAR) network. LTAR is supported by the United States Department of Agriculture . We thank Heidi Peterson and Tom Bruulsema of the International Plant Nutrition Institute for sharing their expertise about NuGIS. Thanks also to Mark Kautz of the LTAR Communications Working Group for graphic design of Fig. 1 c, and to Bruce Vandenberg of the USDA Data Innovations Team for preparing and presenting our data products in the USDA Agricultural Collaborative Research Outcomes System (AgCROS). Thanks to two peer reviewers whose insightful and constructive comments helped to improve this work, and to Jeffrey E. Herrick, Brandon T. Bestelmeyer, Joel R. Brown, Peter Vadas, and Paul L. Spiegal for their helpful input. We are grateful to Noel Gollehon for his encouragement and guidance at the start of the LTAR Manureshed Project.
Publisher Copyright:
© 2020
PY - 2020/6
Y1 - 2020/6
N2 - 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.
AB - 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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U2 - 10.1016/j.agsy.2020.102813
DO - 10.1016/j.agsy.2020.102813
M3 - Article
AN - SCOPUS:85088649328
VL - 182
JO - Agricultural Systems
JF - Agricultural Systems
SN - 0308-521X
M1 - 102813
ER -