INTEGRATED CROP-LIVESTOCK SYSTEMS: LESSONS FROM NEW YORK, BRITISH COLUMBIA, AND THE SOUTH-EASTERN UNITED STATES

Alan FRANZLUEBBERS, Derek HUNT, Gary TELFORD, Shabtai BITTMAN, Quirine KETTERINGS

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Front. Agr. Sci. Eng. ›› 2021, Vol. 8 ›› Issue (1) : 81-96. DOI: 10.15302/J-FASE-2020365
RESEARCH ARTICLE
RESEARCH ARTICLE

INTEGRATED CROP-LIVESTOCK SYSTEMS: LESSONS FROM NEW YORK, BRITISH COLUMBIA, AND THE SOUTH-EASTERN UNITED STATES

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Highlights

• Livestock production in North America has moved to fewer farms with greater inventories

• Land application of livestock manures is a preferred nutrient recycling strategy

• Confined animal feeding operations have challenges to utilize livestock manure sustainably

• Integration of livestock and cropping systems is possible on a farm or among farms

• Nutrient balance is needed for environmental sustainability

Abstract

Livestock production in the United States (US) and Canada is diverse, but shows a common trend in most livestock sectors toward fewer farms producing the majority of animal products despite a large number of farms still small in production scale. The migration to larger and more concentrated animal feeding operations in beef finishing and poultry, swine, and dairy production allows processors to streamline supplies to meet market demand for abundant, low-cost livestock products, whether that be for packaged meat, dairy products, or eggs. With concentration of livestock operations comes the challenge of managing manures. When sufficient land is available and nutrients are needed, livestock manure is an excellent nutrient source and land application is the preferred method of recycling this resource. However, when livestock production is constrained in a geographical area and animal densities are high, manure may become an environmental liability with potentially greater risk for runoff and leaching of nutrients, emission of odors, ammonia, and greenhouse gases, and release to the environment of pathogens and chemicals of emerging concern. Addressing these challenges now and into the future requires learning from mistakes and adopting successful approaches. We describe different levels of integration between livestock and crop producers in New York, British Columbia, and the south-eastern US as learning opportunities to improve economic and environmental sustainability. Examples show that effective solutions should recognize (1) manure has value and is not just a cost, (2) farmers, farm advisors, extension educators, nutrient management planners, crop advisors, nutritionists, state agency personnel, regulators, and university researchers need to be active participants in development of solutions, and (3) change to a sustainable future requires a combination of government regulation and outcome-based incentives.

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Keywords

cropland / dairy manure / nutrient cycling / pastureland / poultry manure / swine manure

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Alan FRANZLUEBBERS, Derek HUNT, Gary TELFORD, Shabtai BITTMAN, Quirine KETTERINGS. INTEGRATED CROP-LIVESTOCK SYSTEMS: LESSONS FROM NEW YORK, BRITISH COLUMBIA, AND THE SOUTH-EASTERN UNITED STATES. Front. Agr. Sci. Eng., 2021, 8(1): 81‒96 https://doi.org/10.15302/J-FASE-2020365

References

[1]
Thornton P K. Livestock production: recent trends, future prospects. Philosophical Transactions of the Royal Society of London. Series B, Biological Sciences, 2010, 365(1554): 2853–2867
CrossRef Pubmed Google scholar
[2]
Porkka M, Kummu M, Siebert S, Varis O. From food insufficiency towards trade dependency: a historical analysis of global food availability. PLoS One, 2013, 8(12): e82714
CrossRef Pubmed Google scholar
[3]
MacDonald J M, Ollinger M E, Nelson K E, Hand C R. Consolidation in U.S. meatpacking. Food and Rural Economics Division, Economic Research Service, USDA. Agricultural Economic Report, 2000, 785. doi:10.22004/ag.econ.34021
[4]
Shields D A. Consolidation and concentration in the U.S. dairy industry. Washington DC: Congressional Research Service, April 2010, 7–5700, R41224. Available at National Agricultural Law Center website on September 26, 2020
[5]
USDA-NASS (National Agricultural Statistics Service). Census of Agriculture. Washington DC: USDA, 2020. Available at USDA website on September 26, 2020
[6]
USDA, Economic Research Service, Food Expenditure Series. Washington DC: USDA, 2020. Available at USDA website on September 26, 2020
[7]
Bureau of Economic Analysis. Gross domestic product by industry. Suitland Maryland USA:Bureau of Economic Analysis, 2020. Available at Bureau of Economic Analysis website on September 26, 2020
[8]
USDA-NASS. 2019 State Agriculture Overview of New York. Washington DC: USDA, 2019. Available at USDA website on September 26, 2020
[9]
Ketterings Q M, Knight J, Ristow P, Swanepoel G, Czymmek K J. Evaluation of dairy and cash grain farmers’ perceptions of the value of manure. Crop Management, 2012, 11(1): 1–8
CrossRef Google scholar
[10]
Swink S N, Ketterings Q M, Chase L E, Czymmek K J, Mekken J C. Past and future phosphorus balances for agricultural cropland in New York State. Journal of Soil and Water Conservation, 2009, 64(2): 120–133
CrossRef Google scholar
[11]
Cela S, Ketterings Q M, Czymmek K J, Soberon M, Rasmussen C N. Characterization of N, P, and K mass balances of dairy farms in New York State. Journal of Dairy Science, 2014, 97: 7614–7632
CrossRef Pubmed Google scholar
[12]
Cela S, Ketterings Q M, Czymmek K, Soberon M, Rasmussen C. Long-term trends of nitrogen and phosphorus mass balances on New York State dairy farms. Journal of Dairy Science, 2015, 98(10): 7052–7070
CrossRef Pubmed Google scholar
[13]
Cela S, Ketterings Q M, Soberon M, Rasmussen C, Czymmek K J. Upper Susquehanna watershed and New York State improvements in nitrogen and phosphorus mass balances of dairy farms. Journal of Soil and Water Conservation, 2017, 72(1): 1–11
CrossRef Google scholar
[14]
Soberon M A, Cela S, Ketterings Q M, Rasmussen C N, Czymmek K J. Changes in nutrient mass balances over time and related drivers for 54 New York State dairy farms. Journal of Dairy Science, 2015, 98(8): 5313–5329
CrossRef Pubmed Google scholar
[15]
United States Department of Agriculture-Environmental Protection Agency (USDA-EPA). Unified national strategy for animal feeding operations. Washington DC: USDA-EPA, 1999. Available at USDA-EPA website on September 26, 2020
[16]
Czymmek K J, Ketterings Q M, Geohring L D, Albrecht G L. The New York phosphorus runoff index. User’s manual and documentation. Ithaca, NY, USA. 2003. Available at Cornell University website on September 26, 2020
[17]
Ketterings Q M, Cela S, Collick A S, Crittenden S J, Czymmek K J. Restructuring the P index to better address P management in New York. Journal of Environmental Quality, 2017, 46(6): 1372–1379
CrossRef Pubmed Google scholar
[18]
Ros M B H, Ketterings Q M, Cela S, Czymmek K J. Evaluating management implications of the New York phosphorus index with farm field information. Journal of Environmental Quality, 2019, 48(4): 1082–1090
CrossRef Pubmed Google scholar
[19]
Ros M B H, Czymmek K J, Ketterings Q M. Combining field phosphorus runoff risk assessments with whole-farm phosphorus balances to guide manure management decisions. Journal of Environmental Quality, 2020, 49(2): 496–508
CrossRef Pubmed Google scholar
[20]
Czymmek K, Ketterings Q M, van Es H, DeGloria S. The New York nitrate leaching index. CSS Extension Publication E03–2. 2003. Available at Cornell University website on September 26, 2020
[21]
Cornell University. Nutrient Management Spear Program at Cornell University. Ithaca: Cornell University, 2002. Available at Cornell University website on September 25, 2020
[22]
USDA-NRCS. Conservation Practice Standard, Nutrient Management 590 for New York. 2013. Available at USDA website on September 26, 2020
[23]
Ketterings Q M, Czymmek K J. P Index as a P awareness tool: documented P use reduction in New York State. Journal of Environmental Quality, 2012, 41(6): 1767–1773
CrossRef Pubmed Google scholar
[24]
Ketterings Q M, Czymmek K J, Swink S N. Evaluation methods for a combined research and extension program used to address starter phosphorus fertilizer use for corn in New York. Canadian Journal of Soil Science, 2011, 91(3): 467–477
CrossRef Google scholar
[25]
Ketterings Q M, Swink S N, Godwin G, Czymmek K J, Albrecht G L. Maize silage yield and quality response to starter phosphorus fertilizer in high phosphorus soils in New York. Journal of Food Agriculture and Environment, 2005, 3(2): 360–365
[26]
Ketterings Q M, Kahabka J E, Reid W S. Trends in phosphorus fertility of New York agricultural land. Journal of Soil and Water Conservation, 2005, 60(1): 10–20
[27]
Cela S, Ketterings Q M, Czymmek K J, Weld J, Beegle D B, Kleinman P J A. Nutrient management planners’ feedback on New York and Pennsylvania phosphorus indices. Journal of Soil and Water Conservation, 2016, 71(4): 281–288
CrossRef Google scholar
[28]
Ketterings Q M. Extension and knowledge transfer; adaptive management approaches for timely impact. Journal of Agricultural Science, 2014, 152(S1): 57–64
CrossRef Google scholar
[29]
Fraser V R D. Regional Snapshot Series: Agriculture. Agricultural economy in the Fraser Valley Regional District, December 2017 update. Chilliwack BC: Fraser Valley Regional District. Available at Fraser Valley Regional District website on September 26, 2020
[30]
Bittman S, Sheppard S C, Poon D, Hunt D E. Phosphorus flows in a peri-urban region with intensive food production: a case study. Journal of Environmental Management, 2017, 187: 286–297
CrossRef Pubmed Google scholar
[31]
Bittman S, Sheppard S C, Poon D, Hunt D E. How efficient is modern peri-urban nitrogen cycling: a case study. Journal of Environmental Management, 2019, 244: 462–471
CrossRef Pubmed Google scholar
[32]
Bittman S, Jones K, Vingarzan R, Hunt D E, Sheppard S C, Tait J, So R, Zhao J. Weekly agricultural emissions and ambient concentrations of ammonia: validation of an emission inventory. Atmospheric Environment, 2015, 113: 108–117
CrossRef Google scholar
[33]
Bittman S, Sheppard S C, Hunt D. Potential for mitigating atmospheric ammonia in Canada. Soil Use and Management, 2017, 33(2): 263–275
CrossRef Google scholar
[34]
Putt A E, MacIsaac E A, Herunter H E, Cooper A B, Selbie D T. Eutrophication forcings on a peri-urban lake ecosystem: context for integrated watershed to airshed management. PLoS One, 2019, 14(7): e0219241
CrossRef Pubmed Google scholar
[35]
Li Y. Forage crop nitrogen recovery and nitrogen field-losses determined on semi-virtual dairy farms under integrated nutrient and crop management scenarios. Dissertation for the Master’s Degree. Canada: University of British Columbia, 2019
[36]
Sullivan C, Poon D. Fraser Valley Soil Nutrient Survey 2012. A follow-up to a 2005 survey of nutrient status of agricultural fields in relation to environmental and agronomic concerns. Vancouver BC: BC Government, 2016. Available at BC Government website on September 26, 2020
[37]
Søgaard H T, Sommer S G, Hutchings N J, Huijsmans J F M, Bussink D W, Nicholson F. Ammonia volatilization from field-applied animal slurry—the ALFAM model. Atmospheric Environment, 2002, 36(20): 3309–3319
CrossRef Google scholar
[38]
Bittman S, Kowalenko C G, Forge T, Hunt D E, Bounaix F, Patni N. Agronomic effects of multi-year surface-banding of dairy slurry on grass. Bioresource Technology, 2007, 98(17): 3249–3258
CrossRef Pubmed Google scholar
[39]
Zhang H, Bittman S, Hunt D E, Bounaix F. Corn response to long-term manure and fertilizer applications on a preceding perennial forage crop. European Journal of Agronomy, 2020, 115: 125990
CrossRef Google scholar
[40]
Zebarth B J, Hii B, Liebscher H, Chipperfield K, Paul J W, Grove G, Szeto S Y. Agricultural land use practices and nitrate contamination in the Abbotsford Aquifer, British Columbia, Canada. Agriculture, Ecosystems & Environment, 1998, 69(2): 99–112
CrossRef Google scholar
[41]
Zebarth B J, Ryan M C, Graham G, Forge T A, Neilsen D. Groundwater monitoring to support development of BMPs for groundwater protection: the Abbotsford‐Sumas aquifer case study. Ground Water Monitoring and Remediation, 2015, 35(1): 82–96
CrossRef Google scholar
[42]
Zhang H, Hunt D E, Bittman S. Animal-based organic amendments and their potential for excessive nitrogen leaching and phosphorus loading. Agronomy Journal, 2019, 111(5): 2207–2217
CrossRef Google scholar
[43]
Russelle M P, Blanchet K M, Randall G W, Everett L E. Characteristics and nitrogen value of stratified bedded pack dairy manure. Crop Management, 2009, 8(1): 1–10
CrossRef Google scholar
[44]
Kowalenko C G. Growing season dry matter and macroelement accumulations in Willamette red raspberry and related soil-extractable macroelement measurements. Canadian Journal of Plant Science, 1994, 74(3): 565–571
CrossRef Google scholar
[45]
Kowalenko C G. Growing season changes in the concentration and distribution of macroelements in Willamette red raspberry plant parts. Canadian Journal of Plant Science, 1994, 74(4): 833–839
CrossRef Google scholar
[46]
Suchy M, Wassenaar L I, Graham G, Zebarth B. High-frequency NO3 isotope (d15N, d18O) patterns in groundwater recharge reveal that short-term land use and climatic changes influence nitrate contamination trends. Hydrology and Earth System Sciences Discussions, 2018, 22(8): 4267–4279
CrossRef Google scholar
[47]
Bittman S, Hunt D E, Kowalenko C G, Chantigny M, Buckley K, Bounaix F. Removing solids improves response of grass to surface-banded dairy manure slurry: a multiyear study. Journal of Environmental Quality, 2011, 40(2): 393–401
CrossRef Pubmed Google scholar
[48]
Bittman S, Liu A, Hunt D E, Forge T A, Kowalenko C G, Chantigny M H, Buckley K. Precision placement of separated dairy sludge improves early phosphorus nutrition and growth in corn (Zea mays L.). Journal of Environmental Quality, 2012, 41(2): 582–591
CrossRef Pubmed Google scholar
[49]
Schröder J J, Vermeulen G D, van der Schoot J R, van Dijk W, Huijsmans J F M, Meuffels G J H M, van der Schans D A. Maize yields benefit from injected manure positioned in bands. European Journal of Agronomy, 2015, 64: 29–36
CrossRef Google scholar
[50]
Pedersen I F, Rubæk G H, Sørensen P. Cattle slurry acidification and application method can improve initial phosphorus availability for maize. Plant and Soil, 2017, 414(1–2): 143–158
CrossRef Google scholar
[51]
Franzluebbers A J. Soil-test biological activity with the flush of CO2: V. Validation of nitrogen prediction for corn production. Agronomy Journal, 2020, 112(3): 2188–2204
CrossRef Google scholar
[52]
Franzluebbers A J. Soil-test biological activity with the flush of CO2: III. Corn yield responses to applied nitrogen. Soil Science Society of America Journal, 2018b, 82(3): 708–721
CrossRef Google scholar
[53]
Lory J A, Massey R E, Zulovich J M, Hoehne J A, Schmidt A M, Carlson M S, Fulhage C D. An assessment of nitrogen-based manure application rates on 39 U.S. swine operations. Journal of Environmental Quality, 2004, 33(3): 1106–1113
CrossRef Pubmed Google scholar
[54]
Eghball B, Gilley J E. Phosphorus and nitrogen in runoff following beef cattle manure or compost application. Journal of Environmental Quality, 1999, 28(4): 1201–1210
CrossRef Google scholar
[55]
Miller J J, Chanasyk D S, Curtis T W, Olson B M. Phosphorus and nitrogen in runoff after phosphorus- or nitrogen-based manure applications. Journal of Environmental Quality, 2011, 40(3): 949–958
CrossRef Pubmed Google scholar
[56]
Novak J M, Watts D W, Hunt P G, Stone K C. Phosphorus movement through a Coastal Plain soils after a decade of intensive swine manure application. Journal of Environmental Quality, 2000, 29(4): 1310–1315
CrossRef Google scholar
[57]
Franzluebbers A J. Short-term C mineralization (aka the flush of CO2) as an indicator of soil biological health. Perspectives in Agriculture, Veterinary Science, Nutrition and Natural Resources, 2018, 13(17): 1–14
CrossRef Google scholar
[58]
Franzluebbers A J, Pehim-Limbu S, Poore M H. Soil-test biological activity with the flush of CO2: IV. Fall-stockpiled tall fescue yield response to applied nitrogen. Agronomy Journal, 2018, 110(5): 2033–2049
CrossRef Google scholar
[59]
Franzluebbers A J, Poore M H. Soil-test biological activity with the flush of CO2: VII. Validating nitrogen needs for fall-stockpiled forage. Agronomy Journal, 2020, 112(3): 2240–2255
CrossRef Google scholar

Supplementary materials

The online version of this article at https://doi.org/10.15302/J-FASE-2020365 contains supplementary materials (Tables S1–S4; Figs. S1–S5).

Compliance with ethics guidelines

Alan Franzluebbers, Derek Hunt, Gary Telford, Shabtai Bittman, and Quirine Ketterings declare that they have no conflicts of interest or financial conflicts to disclose.
This article does not contain any studies with human or animal subjects performed by any of the authors.

RIGHTS & PERMISSIONS

The Author(s) 2020. Published by Higher Education Press. This is an open access article under the CC BY license (http://creativecommons.org/licenses/by/4.0)
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