Scientia Agricultura Sinica ›› 2019, Vol. 52 ›› Issue (20): 3625-3636.doi: 10.3864/j.issn.0578-1752.2019.20.013

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• SPECIAL FOCUS: SOIL WATER AND FERTILIZER MANAGEMENT IN GREENHOUSE VEGETABLE FIELDS • Previous Articles     Next Articles

Effect of Organic Partial Replacement of Inorganic Fertilizers on N2O Emission in Greenhouse Soil

YaJing XI1,2,DongYang LIU1,2,JunYu WANG1,2,XuePing WU2(),XiaoXiu LI1,YinKun LI3(),BiSheng WANG2,MengNi ZHANG2,XiaoJun SONG2,ShaoWen HUANG2   

  1. 1 College of Resource Environment and Tourism, Capital Normal University, Beijing 100037
    2 Institute of Agricultural Resource and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081
    3 Beijing Research Center of Intelligent Equipment for Agriculture, Beijing 100097
  • Received:2019-05-15 Accepted:2019-09-04 Online:2019-10-16 Published:2019-10-28
  • Contact: XuePing WU,YinKun LI E-mail:wuxueping@caas.cn;lykun1218@163.com

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Abstract:

【Objective】 Under the condition of replacing the inorganic fertilizer part with the same amount of nitrogen, the purpose of this study was to study the emission characteristics of greenhouse tomato soil N2O and to explore the environmental factors affecting N2O emissions, which could provide data support and theoretical basis for the N2O emission inventory of the greenhouse vegetable system and its emission reduction potential.【Method】 Taking greenhouse autumn-winter tomato as the research object, the static-chamber method was used to monitor the soil N2O emission, soil temperature and soil water content during the growth period of tomato. The experiment was set 4 treatments, including non-fertilization (CK), single application of organic fertilizer (MN), single application of inorganic fertilizer (CN), and organic partial replacement of inorganic fertilizers (CMN).【Result】 Under the same nitrogen application rate, the total N2O emission under CMN was 4.05 kg·hm -2. Compared with CN and MN, the total N2O emission under CMN decreased by 45.1% and 33.2% , respectively; the emission factor of soil N2O was reduced by 50.0% and 37.5%, respectively; the emission intensity was reduced by 50.0% and 42.1%, respectively. The peak soil N2O of all treated appeared on the first day after fertilization and irrigation, and the discharge was mainly concentrated within 5 days after fertilization and irrigation. The N2O emission flux in greenhouse tomato soil showed significant or extremely significant correlation with the ground temperature of 0-5 cm soil, and showed a significant or extremely significant logarithm function relationship with soil water-filled porosity (WFPS). The peak of soil N2O emission under different fertilization treatments appeared in 60%~80% soil-filled porosity.【Conclusion】 The relationship between the growth and decline of N2O emissions in greenhouse tomato soil was reflected in the changes of temperature and humidity and the type of nitrogen fertilizer input. Reasonable emission reduction measures should be considered based on the above factors. Partial replacement of inorganic fertilizers with organic fertilizers was an important means to increase greenhouse tomato production, to reduce N2O emissions intensity, factor and total N2O emissions increase fertilizer utilization, and to achieve zero growth of fertilizers.

Key words: N2O emission, greenhouse tomato, organic fertilizer, inorganic fertilizer, soil temperature, soil water-filled porosity

Table 1

Greenhouse tomato experiment scheme"

处理
Treatment		 氮总量
Total amount of nitrogen (kg·hm-2)		 施氮量
Nitrogen application rate
CK 0 不施氮 No nitrogen application
CMN 675 375 kg·hm-2无机氮+300 kg·hm-2有机氮
375 kg·hm-2 Inorganic nitrogen+300 kg·hm-2 Organic nitrogen
CN 675 675 kg·hm-2无机氮
675 kg·hm-2Inorganic nitrogen
MN 675 675 kg·hm-2有机氮
675 kg·hm-2 Organic nitrogen

Fig. 1

Dynamic of N2O emission under different N application rates The arrow indicates topdressing fertilizer; A and B represent the base fertilizer stage N2O emission and the emission flux on the 1th day; a, b, c, d indicate changes in N2O emission flux after topdressing fertilizer in flowering stage, fruit expansion stage, harvest stage and final harvest stage"

Table 2

Different treatments of tomato yield and soil N2O emissions, emission factors, emission intensity"

处理
Treatment		 番茄产量
Tomato yield (t·hm-2)		 基肥阶段排放量
Base fertilizer stage emission (kg·hm-2)		 追肥阶段排放量
Topdressing fertilizer stage emission (kg·hm-2)		 排放总量
Total emission
(kg·hm-2)		 排放系数
Emission factor
(%)		 排放强度
Emission intensity (kg·t-1)
CK 29.03±1.33c 0.17±0.06c 0.48±0.02d 0.65±0.03d 0.02
CMN 36.54±1.28a 2.14±0.01b 1.91±0.03c 4.05±0.04c 0.5 0.11
CN 34.00±2.28ab 1.94±0.02b 5.43±0.04a 7.37±0.01a 1.0 0.22
MN 32.56±1.64b 3.56±0.02a 2.50±0.02b 6.06±0.01b 0.8 0.19

Fig. 2

The relationship between N2O emission flux and WFPS a, b, c, d Indicates the four periods of the tomato topdressing fertilizer stage (flowering stage, fruit expansion stage, harvest stage and final harvest stage ). ** Represented significant correlation at 0.01 level, * Represented significant correlation at 0.05 level"

Fig. 3

Relationship between N2O emission flux and 5 cm soil temperature ** Represented significant correlation at 0.01 level, * Represented significant correlation at 0.05 level"

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