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Frontiers of Agricultural Science and Engineering

ISSN 2095-7505

ISSN 2095-977X(Online)

CN 10-1204/S

Postal Subscription Code 80-906

Front. Agr. Sci. Eng.    2023, Vol. 10 Issue (3) : 341-362    https://doi.org/10.15302/J-FASE-2023509
REVIEW
LIVESTOCK AND POULTRY MANURE MANAGEMENT FROM THE PERSPECTIVE OF CARBON NEUTRALITY IN CHINA
Leli ZHANG1,2, Reaihan E1,2, Mahmoud M. ALI1,2,3, Hongjian LIN4, Shuai ZHANG5, Shuqin JIN6, Zhiping ZHU7, Jianjun HU8, Yiqing YAO9, Yong SUN10, Shuiping YAN11, Zhidan LIU1,2()
1. Laboratory of Environment-Enhancing Energy (E2E), College of Water Resources and Civil Engineering, China Agricultural University, Beijing 100083, China
2. Key Laboratory of Agricultural Engineering in Structure and Environment, Ministry of Agriculture and Rural Affairs, Beijing 100083, China
3. Agricultural Engineering Research Institute, Agricultural Research Center, Giza 12311, Egypt
4. College of Biosystems Engineering and Food Science, Zhejiang University, Hangzhou 310058, China
5. College of Animal Science and Technology, China Agricultural University, Beijing 100193, China
6. Research Center for Rural Economy, Ministry of Agriculture and Rural Affairs, Beijing 100810, China
7. Institute of Environmental and Sustainable Development in Agriculture, Chinese Academy of Agriculture Sciences, Beijing 100081, China
8. College of Mechanical & Electrical Engineering, Henan Agricultural University, Zhengzhou 450002, China
9. College of Mechanical and Electrical Engineering, Northwest A&F University, Yangling 712100, China
10. College of Engineering, Northeast Agricultural University, Harbin 150030, China
11. College of Engineering, Huazhong Agricultural University, Wuhan 430070, China
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Abstract

● Carbon reduction potential of manure treatment technologies was summarized.

● Accounting methodologies of carbon emission and footprint of manure were analyzed.

● The quote of carbon trading market at home and abroad was analyzed.

● Some points for the boost of potential of manure carbon trading were advised.

The rapid growth of the livestock and poultry production in China has led to a rise in manure generation, which contributes to the emissions of GHGs (greenhouse gases including CH4, N2O and CO2) and other harmful gases (NH3, H2S). Reducing and managing carbon emissions has become a critical global environmental imperative due to the adverse impacts of GHGs. Unlike previous reviews that focused on resource recovery, this work provides an unique insight of transformation from resource-oriented manure treatment to integration of resource recovery with pollution reduction, carbon accounting and trading, focusing on the sustainable development of manure management system. Considering the importance of accounting methodologies for carbon emission and trading system toward carbon neutrality society, suggestions and strategies including attaching high importance to the development of more accuracy accounting methodologies and more practical GHG emission reduction methodologies are given in this paper. This work directs the establishment of carbon reduction methodologies and the formulation of governmental policies for livestock and poultry manure management system in China.

Keywords valorization of animal manure      manure management      carbon emission      carbon footprint      methodology      carbon trading     
Corresponding Author(s): Zhidan LIU   
Just Accepted Date: 28 July 2023   Online First Date: 07 September 2023    Issue Date: 20 September 2023
 Cite this article:   
Leli ZHANG,Reaihan E,Mahmoud M. ALI, et al. LIVESTOCK AND POULTRY MANURE MANAGEMENT FROM THE PERSPECTIVE OF CARBON NEUTRALITY IN CHINA[J]. Front. Agr. Sci. Eng. , 2023, 10(3): 341-362.
 URL:  
https://academic.hep.com.cn/fase/EN/10.15302/J-FASE-2023509
https://academic.hep.com.cn/fase/EN/Y2023/V10/I3/341
Fig.1  Relationships between livestock and poultry manure treatment technologies, and carbon accounting and trading systems in the context of low-carbon agriculture.
Fig.2  Negative effects on the environment caused by the indiscriminate use of livestock and poultry manure.
Fig.3  Schematic (a) and comparative analysis (b) of livestock and poultry manure treatment technologies. This graph is drawn by the authors with comprehensive reference to a number of literature[922,3368].
Regions Livestock or poultry CH4 N2O Regions Livestock or poultry CH4 N2O
Northern China Cow 7.46 1.846 Central southern China Cow 8.45 1.710
Non-dairy cattle 2.82 0.794 Non-dairy cattle 4.72 0.805
Sheep 0.15 0.093 Sheep 0.34 0.106
Goat 0.17 0.093 Goat 0.31 0.106
Pig 3.12 0.227 Pig 5.85 0.157
Poultry 0.01 0.007 Poultry 0.02 0.007
Northeastern China Cow 2.23 1.096 Southwestern China Cow 6.51 1.884
Non-dairy cattle 1.02 0.913 Non-dairy cattle 4.72 0.691
Sheep 0.15 0.057 Sheep 0.34 0.064
Goat 0.16 0.057 Goat 0.31 0.064
Pig 1.12 0.266 Pig 5.85 0.159
Poultry 0.01 0.007 Poultry 0.02 0.007
Eastern China Cow 8.33 2.065 Northwestern China Cow 5.93 1.447
Non-dairy cattle 3.31 0.846 Non-dairy cattle 1.86 0.545
Sheep 0.26 0.113 Sheep 0.28 0.074
Goat 0.28 0.113 Goat 0.32 0.074
Pig 5.08 0.175 Pig 1.38 0.195
Poultry 0.02 0.007 Poultry 0.01 0.007
Tab.1  GHG emission coefficients* of livestock and poultry manure management system in different regions of Chinese mainland (kg·head−1·yr−1)[69]
Method Advantage Disadvantage Suitable for circumstance Classification*
Mass-balance method Reflect the actual carbon emissions
Distinguish the differences between various facilities
Distinguish the differences between entire and partial equipment
Difficult to avoidsystematic errors When carbon emission sources are complex
When equipment is constantly updated
A
OECD Calculation method is simple Accuracy of the calculation is not high Requirement for accuracy is not highCH4 emissions from ruminants A
IPCC Comprehensive calculation range; more accurate (in Tier-3) Poor ability to handle the changes in the emission system When emission sources are not complex or the complexity is negligible Both A and B
I-O Account carbon footprint and environmental impact of a product or service more completely Weak timeliness Macroscopic levels like countries, departments, enterprises B
LCA The carbon footprint and environmental impact of a product or service can be assessed more accurately
The accuracy of the scope can be set according to specific goals
Boundary setting is based on strong subjectivity Micro levels of specific products or services B
Tab.2  Summary of carbon emission accounting methods[86]
Mandatory carbon trading market Voluntary carbon trading market
Executor Upper organization Organizations and individuals with social responsibilities
Trading mode Cap and trade More flexible and unrestricted by regulations or the Kyoto Protocol
Characteristics Policy formulation defines the total amount of GHGs
Structures and current situation of the enterprise determine its specific emissions
Purchase carbon credit lines to offset its emissions
Apply for certification of voluntary emission reduction (VER) projects to get VERSell excess emission quota for profits
Typical systemand standards EU ETS (European Union)
K ETS (South Korea’s)
NZ ETS (New Zealand’s)
Gold Standard (GS)
Verified Carbon Standard
The Standard for VER
VER + and so on
Tab.3  Main differences between the two main modes of the global carbon trading market
Fig.4  Development of the carbon trading market in China.
Fig.5  Trading mechanisms of the carbon quota trading market and Chinese-certified emission reduction (CCER) trading market.
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