Scientia Agricultura Sinica ›› 2020, Vol. 53 ›› Issue (24): 5050-5062.doi: 10.3864/j.issn.0578-1752.2020.24.008

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

Greenhouse Gas Emission During the Initial Years After Rice Paddy Conversion to Vegetable Cultivation

WU Lei1(),HE ZhiLong2,TANG ShuiRong3,WU Xian2,ZHANG WenJu1,HU RongGui2()   

  1. 1Institute of Agricultural Resources and Regional Planning, Chinese Academy of Agricultural Sciences, Beijing 100081
    2College of Recourses and Environment, Huazhong Agricultural University, Wuhan 430070
    3College of Tropical Crops, Hainan University, Haikou 570228
  • Received:2020-04-01 Accepted:2020-06-03 Online:2020-12-16 Published:2020-12-28
  • Contact: RongGui HU E-mail:wulei01@caas.cn;rghu@mail.hzau.edu.cn

Abstract:

【Objective】In recent years, with the rapid development of social economy, the improvement of people’s living standards and shifting diets and the increasing demands of vegetables result in a considerable share of rice paddy fields conversion to vegetable production in China, thus influencing soil carbon and nitrogen cycling and associated greenhouse gas (GHG) emissions. Therefore, it is necessary to investigate the impacts of land-use conversion from rice into vegetable cultivation on methane (CH4) and nitrous oxide (N2O) emissions and their key regulating factors, particularly during initial period upon conversion. 【Method】In this study, six rice paddies subjected to long-term double-rice planting were chosen, and the half of them were converted into vegetable cultivation (Veg) and the remaining still for rice production (Rice), with three replicates of each treatment. The Veg and Rice were managed according to local practices. The fluxes of CH4 and N2O from the rice paddy and converted vegetable fields were measured with static chambers from December 2012 to December 2015, so as to investigate the characteristics and inter-annual variation of CH4 and N2O emissions and to identify the key factors regulating the two GHGs during the initial period upon conversion. 【Result】Rice paddy acted as an important source of CH4, and CH4 emission was significantly lower in the first year (183.91 kg CH4-C·hm-2?a-1) relative to the later two years (241.56-371.50 kg CH4-C·hm-2?a-1), mainly attributed to enhanced precipitation increasing soil water content during the latter two years. Conversion from rice to vegetable cultivation substantially reduced CH4 emission from Veg by 83%-100% as compared to Rice over the study period. Annual CH4 emissions from Veg were significantly higher in the first year (31.22 kg CH4-C·hm-2) relative to any later years (0.45-0.89 kg CH4-C·hm-2), suggesting that this land-use conversion had strong legacy effect on CH4 emission. Paddy soil acted as a minor source of N2O (1.35-3.49 kg N2O-N·hm-2?a-1). Rice conversion to vegetable cultivation led to substantial N2O emission, particularly in the first year during which the cumulative emissions were significantly larger (95.12 kg N2O-N·hm-2) than that in the second (38.28 kg N·hm-2) and third year (40.07 kg N2O-N·hm-2). N2O fluxes from Veg were significantly and positively related to soil heterotrophic respiration rates (Rh), and the dependence of N2O fluxes on Rh was greater in the first year relative to the subsequent two years. These results suggested that soil organic matter mineralization contributed to N2O emissions during the first year upon land-use conversion from rice to vegetable production. Land-use conversion from rice to vegetable cultivation significantly increased the global warming potential (GWP) of Veg by 390% and 98% in the first and second year, respectively, relative to Rice, primarily due to the increased GWP of N2O emission far outweighing the decreased GWP of CH4 emission. In contrast, the GWP of rice (14.84±1.39 Mg CO2-eq·hm-2) was similar to that of Veg (16.72±3.25 Mg CO2-eq·hm-2) in the third year after conversion, due to the decreased GWP of CH4 emission fully offsetting the increased GWP of N2O emission. These results suggested that land-use conversion from rice to vegetable cultivation had significant impacts on the GWP only at the initial stage upon conversion. 【Conclusion】Land-use conversion from rice to vegetable cultivation significantly decreased CH4 while increasing N2O emissions over the whole study period, and increased the GWP only in the first and second year upon conversion. Soil organic matter mineralization significantly contributed to increased N2O emission from the converted vegetable field. This study suggested that soil GHG emissions in the first years upon conversion were the most important, therefore, which should be considered when evaluating the environmental consequences of land-use conversion. This study also helped us develop effective options to alleviate the effects of land-use conversion on GHG emissions, and for sustainable agricultural production and GHG mitigation.

Key words: rice paddy, vegetable field, land-use conversion, CH4, N2O, global warming potential (GWP)

Table 1

Overview of the fertilization practices of double-rice and vegetable fields during the observation period from 2012 to 2015"

稻田 Rice paddy 菜地 Vegetable field
施肥时间
Fertilization date
肥料类型
Fertilizer type
施肥量
Rate (kg N·hm-2)
施肥时间
Fertilization date
肥料类型
Fertilizer types
施肥量
Rates (kg N·hm-2)
早稻 Early rice 红菜苔 Red cabbage
3 May 2013 尿素 Urea 60 8 Dec 2012 复合肥* Compound fertilizer 120
27 May 2013 尿素 Urea 36 2 Mar 2013 尿素 Urea 80
1 Jul 2013 尿素 Urea 24
辣椒 Pepper
晚稻 Late rice 18 Apr 2013 复合肥 Compound fertilizer 90
14 Jul 2013 尿素 Urea 75 16 Jun 2013 尿素 Urea 60
1 Aug 2013 尿素 Urea 45
7 Sep 2013 尿素 Urea 30 白萝卜 Radish
14 Sep 2013 复合肥 Compound fertilizer 120
早稻Early rice 11 Nov 2013 尿素 Urea 80
6 May 2014 尿素 Urea 60
17 May 2014 尿素 Urea 36 空心菜 Water spinach
27 Jun 2014 尿素 Urea 24 17 Apr 2014 复合肥 Compound fertilizer 80
10 May 2014 尿素 Urea 50
晚稻Late rice 27 Jun 2014 尿素 Urea 50
24 Jul 2014 尿素 Urea 75 24 Aug 2014 尿素 Urea 20
31 Jul 2014 尿素 Urea 45
10 Sep 2014 尿素 Urea 30 白萝卜 Radish
6 Sep 2014 复合肥 Compound fertilizer 120
早稻Early rice 30 Oct 2014 尿素 Urea 80
27 Apr 2015 尿素 Urea 60
6 May 2015 尿素 Urea 36 辣椒 Pepper
25 Jun 2015 尿素 Urea 24 16 Apr 2015 复合肥 Compound fertilizer 90
15 Jul 2015 尿素 Urea 60
晚稻Late rice
20 Jul 2015 尿素 Urea 75 白萝卜 Radish
28 Jul 2015 尿素 Urea 45 2 Oct 2015 复合肥 Compound fertilizer 120
7 Sep 2015 尿素 Urea 30 29 Oct 2015 尿素 Urea 80
总氮用量 Total amount 810 总氮用量Total amount 1300

Fig. 1

Dynamics of precipitation and air temperature during the observation period"

Table 2

Soil organic carbon (SOC) and organic nitrogen (SON) contents, bulk density and pH of the 0-20 cm layer in double-rice and vegetable fields initially and 3 years later"

土壤有机碳 SOC (g?kg-1) 土壤有机氮 SON (g?kg-1) 容重 Bulk density (g?cm-3) pH
Dec 2012
Rice 18.7 ± 1.0a 2.04 ± 0.28a 1.03 ± 0.09b 5.48 ± 0.29a
Veg 18.9 ± 1.2a 2.00 ± 0.36a 1.01 ± 0.07b 5.40 ± 0.18a
Dec 2015
Rice 19.1 ± 0.6a 2.12 ± 0.62a 1.01 ± 0.02b 5.39 ± 0.37a
Veg 17.2 ± 0.9b 1.74 ± 0.51b 1.39 ± 0.15a 4.34 ± 0.29b

Fig. 2

Changes of soil properties in the double-rice and vegetable fields during the observation period Rice and Veg represent rice paddy and vegetable field, respectively; Values denote as means ± standard errors of three replicates; * Indicates significant difference between rice paddy and vegetable field in the same year at P<0.05 level; Different letters indicate significant difference among years for the same land-use type at P<0.05 level. The same as Fig. 3, Fig. 4 and Fig. 7"

Fig. 3

Changes of fluxes and annual cumulative emissions of CH4 from double-rice and vegetable fields during the observation period"

Fig. 4

Changes of fluxes and annual cumulative emissions of N2O from double-rice and vegetable fields during the observation period"

Fig. 5

The relationship between CH4 fluxes, and soil temperature and soil water content in double-rice field"

Fig. 6

Relationship between the fluxes of N2O and soil heterotrophic respiration from vegetable field"

Fig. 7

Cumulative emissions of CH4 and N2O from rice and vegetable fields and the associated global warming potential"

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