Scientia Agricultura Sinica ›› 2023, Vol. 56 ›› Issue (10): 1935-1948.doi: 10.3864/j.issn.0578-1752.2023.10.010

• SOIL & FERTILIZER·WATER-SAVING IRRIGATION·AGROECOLOGY & ENVIRONMENT • Previous Articles     Next Articles

Effects of Biochar Combined with Dicyandiamide on Greenhouse Gases Emissions from Facility Vegetable Soil

SONG BoYing1,2(), GUO YanJie1,2,4(), WANG WenZan1,2, LÜ ZeNan1,2, ZHAO YuQing1,2, LIU Lu1,2, ZHANG LiJuan1,2,3()   

  1. 1 College of Resources and Environmental Sciences, Hebei Agricultural University, Baoding 071001, Hebei
    2 Key Laboratory for Farmland Eco-Environment of Hebei Province, Baoding 071001, Hebei
    3 Collaborative Innovation Center for Vegetable Industry of Hebei, Baoding 071001, Hebei
    4 State Key Laboratory of North China Crop Improvement and Regulation, Baoding 071001, Hebei
  • Received:2022-04-13 Accepted:2022-07-12 Online:2023-05-16 Published:2023-05-17

Abstract:

【Objective】This paper aimed to explore the comprehensive effects of biochar, dicyandiamide (DCD) and their combined application on the greenhouse gas (N2O, CO2 and CH4) emissions from facility soil, so as to provide a scientific basis for reducing the greenhouse gas emissions and green development of facility vegetable production system.【Method】In this study, the facility vegetable production system was used as the research object, and a total of six treatments were set up, including no nitrogen application (CK), traditional nitrogen application (CN), recommended nitrogen application (RN), recommended nitrogen application+biochar(RNB), recommended nitrogen application + DCD (RND), and recommended nitrogen application+biochar+ DCD(RNBD). A pot experiment method was applied to analyze the effects of soil greenhouse gas emissions, and the difference in greenhouse gas intensity (GHGI) and global warming potential (GWP) under different treatments.【Result】Compared with the CN treatment, the rape yield decreased by 2.9%-29.3% under the recommend nitrogen treatments (RN, RN, RND and RNBD). However, under the same nitrogen application rate, the rape yield increased by 34.4% in the treatment of recommend nitrogen combined with biochar and DCD (RNBD), indicating that biochar and DCD showed a synergistic effect on rape yield increase (P<0.05). The recommend nitrogen treatments reduced the soil N2O emissions by 29.4%-76.5% in comparation with the CN treatment, especially the RND treatment showed the best effect. However, the recommend nitrogen treatments showed little effect on soil CO2 and CH4 emissions. Compared with the CN treatment, the total GWP under the recommended nitrogen treatments decreased by 4.3%-51.2%, and the RND treatment showed the best emission-reduction effect. In terms of GHGI, the difference among the recommended nitrogen treatments was not significant (P>0.05), and the RND treatment also showed the best emission-reduction effect.【Conclusion】Under the same nitrogen application rate, the application of biochar alone or DCD alone had little effect on rape yield, but the combination of biochar and DCD could significantly increase the rape yield. Additionally, the combination of biochar and DCD could reduce the cumulative greenhouse gas emissions and GWP, but it was not superior to single application of DCD in the facility vegetable field.

Key words: biochar, DCD, facility vegetable field, rape (Brassica campestris L.), greenhouse gas emissions intensity, global warming potential

Table 1

Application amounts of nitrogen, biochar and DCD in different treatments"

处理
Treatment
缩写
Abbreviation
施氮量
Nitrogen application (kg·hm-2)
生物炭施用量
Biochar application (t·hm-2)
双氰胺施用量
DCD application (kg·hm-2)
不施氮对照 No N application CK 0 0 0
传统施氮 Traditional N application CN 450 0 0
推荐施氮 Recommended N application RN 375 0 0
推荐施氮+生物炭 Recommended N application + biochar RNB 375 30 0
推荐施氮+DCD Recommended N application +DCD RND 375 0 56.25
推荐施氮+生物炭+DCD Recommended N application + biochar + DCD RNBD 375 30 56.25

Fig. 1

The rape yield of different treatments"

Fig. 2

Variation of soil N2O emission flux in each treatment"

Table 2

Repeated measured analysis of variance (ANOVA) for the soil greenhouse gases emission in different treatments"

温室气体
Greenhouse gases
因素
Factor
自由度
df
标准差
MS
F检验
F test
P
P value
N2O 处理 Treatment 5 9131.522 28.719 <0.01
时间 Time 13 5749.817 62.541 <0.01
处理×时间Treatment×Time 65 1150.455 12.513 <0.01
CO2 处理 Treatment 5 1314.678 4.398 <0.01
时间 Time 13 4937.243 24.537 <0.01
处理×时间Treatment×Time 65 414.608 2.061 <0.01
CH4 处理 Treatment 5 0.013 45.888 <0.01
时间 Time 13 0.015 39.156 <0.01
处理×时间Treatment×Time 65 0.012 31.413 <0.01

Fig. 3

Variation of soil CO2 emission flux in each treatment"

Fig. 4

Variation of soil CH4 emission flux in each treatment"

Fig. 5

Cumulative emission of greenhouse gases by soil treatment"

Table 3

GWP and GHGI by treatment"

处理
Treatment
N2O GWP
(kg·hm-2)
CO2 GWP
(kg·hm-2)
CH4 GWP
(kg·hm-2)
GWP
(kg·hm-2)
GHGI
(kg·kg-1)
CK 17.4±2.3 c 351.7±59.4 ab -9.0±2.6 a 360.0±60.4 abc 0.6±0.1 a
CN 76.7±23.6 a 424.9±140.4 a -12.4±5.6 a 489.2±168.9 a 0.3±0.1 bc
RN 40.8±7.4 b 440.4±17.8 a -12.8±1.1 a 468.4±11.1 ab 0.5±0.0 ab
RNB 51.7±18.3 b 345.3±96.5 ab -8.1±2.4 a 388.9±115.2 abc 0.4±0.1 b
RND 16.4±0.7 c 229.2±50.4 b -7.2±0.3 a 238.3±49.9 c 0.2±0.0 c
RNBD 16.6±2.3 c 288.2±49.8 ab -8.8±2.5 a 296.0±46.0 bc 0.2±0.0 c
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