NUTRIENT USE EFFICIENCY AND LOSSES OF INDUSTRIAL FARMS AND MIXED SMALLHOLDINGS: LESSONS FROM THE NORTH CHINA PLAIN

Yifei MA, Ling ZHANG, Zhaohai BAI, Rongfeng JIANG, Yong HOU, Lin MA

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Front. Agr. Sci. Eng. ›› 2021, Vol. 8 ›› Issue (1) : 58-71. DOI: 10.15302/J-FASE-2020371
RESEARCH ARTICLE
RESEARCH ARTICLE

NUTRIENT USE EFFICIENCY AND LOSSES OF INDUSTRIAL FARMS AND MIXED SMALLHOLDINGS: LESSONS FROM THE NORTH CHINA PLAIN

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Highlights

• Degree of integration of crop and livestock was insufficient on mixed smallholdings.

• Liquid manure discharges on industrial farms hamper the closing of nutrient loops.

• Coupling with local crop farms is encouraged to achieve integration of crop-livestock systems.

Abstract

The proportion of industrial livestock in China has increased over the past 30 years, which increases animal performance but causes the decoupling of crop and livestock production. Here, we aimed to quantify nutrient flows, nutrient use efficiency, and nutrient losses in different livestock systems in the North China Plain based on the NUFER-farm model. Activity data were collected by face-to-face surveys on pig and dairy (41 livestock farms) during 2016–2018. The two systems included industrial farms and mixed smallholdings. In mixed smallholdings, 4.0% and 9.6% of pig and dairy feed dry matter (DM) were derived from household farmland, but 4.8% and 9.3% of manure DM recycled to household farmland. Nutrient use efficiency in industrial farms was higher than in mixed smallholdings at animal level, herd level, and system level. To produce 1 kg N and P in animal products, nutrient losses in industrial pig farms (2.0 kg N and 1.3 kg P) were lower than in mixed pig smallholdings, nutrient losses in industrial dairy farms (2.7 kg N and 2.2 kg P) were slightly higher than in mixed dairy smallholdings. Liquid manure discharge in industrial farms was the main losses pathway in contrast to mixed smallholdings. This study suggests that feed localization can reduce nutrient surpluses at the district level. It is necessary to improve manure management and increase the degree of integrated crop-livestock in smallholdings. In industrial farms, it is desirable to increase the liquid manure recycling ratio through cooperating livestock and crop production at the district level.

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Keywords

industrial farms / mixed smallholdings / pig / dairy / nutrient management

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Yifei MA, Ling ZHANG, Zhaohai BAI, Rongfeng JIANG, Yong HOU, Lin MA. NUTRIENT USE EFFICIENCY AND LOSSES OF INDUSTRIAL FARMS AND MIXED SMALLHOLDINGS: LESSONS FROM THE NORTH CHINA PLAIN. Front. Agr. Sci. Eng., 2021, 8(1): 58‒71 https://doi.org/10.15302/J-FASE-2020371

References

[1]
Bai Z, Ma L, Jin S, Ma W, Velthof G L, Oenema O, Liu L, Chadwick D, Zhang F. Nitrogen, phosphorus, and potassium flows through the manure management chain in China. Environmental Science & Technology, 2016, 50(24): 13409–13418
CrossRef Pubmed Google scholar
[2]
Bai Z H, Ma L, Qin W, Chen Q, Oenema O, Zhang F S. Changes in pig production in China and their effects on nitrogen and phosphorus use and losses. Environmental Science & Technology, 2014, 48(21): 12742–12749
CrossRef Pubmed Google scholar
[3]
Bai Z H, Ma L, Oenema O, Chen Q, Zhang F S. Nitrogen and phosphorus use efficiencies in dairy production in china. Journal of Environmental Quality, 2013, 42(4): 990–1001
CrossRef Pubmed Google scholar
[4]
Bai Z, Ma W, Ma L, Velthof G L, Wei Z, Havlík P, Oenema O, Lee M R F, Zhang F. China’s livestock transition: driving forces, impacts, and consequences. Science Advances, 2018, 4(7): eaar8534
CrossRef Pubmed Google scholar
[5]
Strokal M, Kroeze C, Wang M, Bai Z, Ma L. The MARINA model (Model to Assess River Inputs of Nutrients to seAs): model description and results for China. Science of the Total Environment, 2016, 562: 869–888
CrossRef Pubmed Google scholar
[6]
Bai Z, Li X, Lu J, Wang X, Velthof G L, Chadwick D, Luo J, Ledgard S, Wu Z, Jin S, Oenema O, Ma L, Hu C. Livestock housing and manure storage need to be improved in China. Environmental Science & Technology, 2017, 51(15): 8212–8214
CrossRef Pubmed Google scholar
[7]
Ministry of Agriculture and Rural Affairs of the People’s Republic of China. China Animal Husbandry and Veterinary Yearbook. Beijing: China Agriculture Press, 2018 (in Chinese)
[8]
Cheng Y S, Hu C S, Chen S Y, Lei Y P, Li H J. Design and case study of the operational system of precision planting. Nongye Gongcheng Xuebao (Beijing), 2004, 20(6): 149–154 (in Chinese)
[9]
Schröder J J, Aarts H F M, ten Berge H F M, van Keulen H, Neeteson J J. An evaluation of whole-farm nitrogen balances and related indices for efficient nitrogen use. European Journal of Agronomy, 2003, 20(1–2): 33–44
CrossRef Google scholar
[10]
Tittonell P, van Wijk M T, Rufino M C, Vrugt J A, Giller K E. Analysing trade-offs in resource and labour allocation by smallholder farms using inverse modelling techniques: a case-study from Kakamega district, western Kenya. Agricultural Systems, 2007, 95(1–3): 76–95
CrossRef Google scholar
[11]
Hilhorst G J, Oenema J, Van Keulen H. Nitrogen management on experimental dairy farm ‘De Marke’; farming system, objectives and results. NJAS-Wageningen Journal of Life Sciences, 2001, 49(2–3): 135–151
CrossRef Google scholar
[12]
Aarts H F M, Habekotté B, van Keulen H. Nitrogen (N) management in the ‘De Marke’ dairy farming system. Nutrient Cycling in Agroecosystems, 2000, 56(3): 231–240
CrossRef Google scholar
[13]
Aarts H F M. Resource management in a ‘De Marke’ dairy farming system. Dissertation for the Doctoral Degree. Wageningen, the Netherlands: Wageningen University, 2000
[14]
Zhao Z Q, Bai Z H, Wei S, Ma W Q, Wang M R, Kroeze C, Ma L. Modeling farm nutrient flows in the North China Plain to reduce nutrient losses. Nutrient Cycling in Agroecosystems, 2017, 108(2): 231–244
CrossRef Google scholar
[15]
Ma Y F. Nitrogen and phosphorus flows characteristics in “soil–crop–livestock” system in the typical county in North China Plain. Dissertation for the Master’s Degree. Beijing: China Agricultural University, 2015 (in Chinese)
[16]
Vida E, Tedesco D E A. The carbon footprint of integrated milk production and renewable energy systems—a case study. Science of the Total Environment, 2017, 609: 1286–1294
CrossRef Pubmed Google scholar
[17]
van Grinsven H J M, ten Berge H F M, Dalgaard T, Fraters B, Durand P, Hart A, Hofman G, Jacobsen B H, Lalor S T J, Lesschen J P, Osterburg B, Richards K G, Techen A K, Vertès F, Webb J, Willems W J. Management, regulation and environmental impacts of nitrogen fertilization in northwestern Europe under the Nitrates Directive; a benchmark study. Biogeosciences, 2012, 9(12): 5143–5160
CrossRef Google scholar
[18]
Ma L, Guo J H, Velthof G L, Velthof G L, Li Y M, Chen Q, Ma W Q, Oenema O, Zhang F S. Impacts of urban expansion on nitrogen and phosphorus flows in the food system of Beijing from 1978 to 2008. Global Environmental Change, 2014, 28(1): 192–204
CrossRef Google scholar
[19]
Ma L, Velthof G L, Wang F H, Qin W, Zhang W F, Liu Z, Zhang Y, Wei J, Lesschen J P, Ma W Q, Oenema O, Zhang F S. Nitrogen and phosphorus use efficiencies and losses in the food chain in China at regional scales in 1980 and 2005. Science of the Total Environment, 2012, 434(18): 51–61
CrossRef Pubmed Google scholar
[20]
Hou Y, Velthof G L, Oenema O. Mitigation of ammonia, nitrous oxide and methane emissions from manure management chains: a meta-analysis and integrated assessment. Global Change Biology, 2015, 21(3): 1293–1312
CrossRef Pubmed Google scholar
[21]
Wei S, Bai Z H, Chadwick D, Hou Y, Qin W, Zhao Z Q, Jiang R F, Ma L. Greenhouse gas and ammonia emissions and mitigation options from livestock production in peri-urban agriculture: Beijing – A case study. Journal of Cleaner Production, 2018, 178: 515–525
CrossRef Google scholar
[22]
Food and Agriculture Organization of the United Nations (FAO). How to Feed the World in 2050. Available at FAO website on February 20, 2020
[23]
Amery F, Schoumans O F. Agricultural phosphorus legislation in Europe. Merelbeke, Belgium:Institute for Agricultural and Fisheries Research, ILVO, 2014, 45
[24]
Bai Z, Lee M R F, Ma L, Ledgard S, Oenema O, Velthof G L, Ma W, Guo M, Zhao Z, Wei S, Li S, Liu X, Havlík P, Luo J, Hu C, Zhang F. Global environmental costs of China’s thirst for milk. Global Change Biology, 2018, 24(5): 2198–2211
CrossRef Pubmed Google scholar
[25]
Li Q, Shi M, Shi C, Liu D, Piao X, Li D, Lai C. Effect of variety and drying method on the nutritive value of corn for growing pigs. Journal of Animal Science and Biotechnology, 2014, 5(1): 18
CrossRef Pubmed Google scholar
[26]
Oenema O. Nitrogen budgets and losses in livestock systems. International Congress, 2006, 1293: 262–271
[27]
Poulsen H D, Jongbloed A W, Latimier P, Fernández J A. Phosphorus consumption, utilisation and losses in pig production in France, The Netherlands and Denmark. Livestock Production Science, 1999, 58(3): 251–259
CrossRef Google scholar
[28]
Velthof G L, Oudendag D, Witzke H P, Asman W A H, Klimont Z, Oenema O. Integrated assessment of nitrogen losses from agriculture in EU-27 using MITERRA-EUROPE. Journal of Environmental Quality, 2009, 38(2): 402–417
CrossRef Pubmed Google scholar
[29]
Wang H L, Long W T, Chadwick D, Velthof G L, Oenema O, Ma W Q, Wang J J, Qin W, Hou Y, Zhang F S. Can dietary manipulations improve the productivity of pigs with lower environmental and economic cost? A global meta-analysis. Agriculture, Ecosystems & Environment, 2020, 289: 106748
CrossRef Google scholar
[30]
Garrett R D, Ryschawy J, Bell L W, Cortner O, Ferreira J, Garik A V N, Gil J D B, Klerkx L, Moraine M, Peterson C A, dos Reis J C, Valentim J F. Drivers of decoupling and recoupling of crop and livestock systems at farm and territorial scales. Ecology and Society, 2020, 25(1): art24
CrossRef Google scholar
[31]
Wei S, Bai Z H, Wu D M, Jiang R F, Xia L J, Ma L. Temporal and spatial characteristics of nitrogen and phosphorus cycling and environmental losses in the “soil-feed-dairy” production system in Beijing. Chinese Journal of Eco-Agriculture, 2017, 25(3): 316–327 (in Chinese)
[32]
Powell J M, Macleod M, Vellinga T V, Opio C, Falcucci A, Tempio G, Steinfeld H, Gerber P. Feed-milk-manure nitrogen relationships in global dairy production systems. Livestock Science, 2013, 152(2–3): 261–272
CrossRef Google scholar
[33]
van Keulen H, Aarts H F M, Habekotté B, van der Meer H G, Spiertz J H J. Soil-plant-animal relations in nutrient cycling: the case of dairy farming system ‘De Marke’. European Journal of Agronomy, 2000, 13(2–3): 245–261
CrossRef Google scholar
[34]
Bai Z H. The resources requirement, nitrogen and phosphorus use and losses in the main livestock production system in China. Beijing: China Agricultural University, 2015 (in Chinese)
[35]
Shechtman O. The coefficient of variation as a measure of sincerity of effort of grip strength, Part II: sensitivity and specificity. Journal of Hand Therapy, 2001, 14(3): 188–194
CrossRef Pubmed Google scholar

Acknowledgements

This study was funded by the National Natural Science Foundation of China (31772393), the National Key Research and Development Program of China (2016YFD0200401), and the National Key Research and Development Program of China funded by the Ministry of Science and Technology of the People's Republic of China (2016YFE0103100). The results and conclusions are those solely of the authors.

Compliance with ethical guidelines

Yifei Ma, Ling Zhang, Zhaohai Bai, Rongfeng Jiang, Yong Hou, and Lin Ma declare that they have no conflicts of interest or financial conflicts to disclose. All applicable institutional and national guidelines for the care and use of animals were followed.

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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