有机肥替代下广东省粮蔬轮作模式N2O排放特征研究

Nitrous oxide emissions from the patterns of grain and vegetable rotation in Guangdong province under organic fertilizer substitution

  • 摘要: 探索有机肥替代措施在广东省气候湿热多雨、土壤酸化、复种指数极高情况下土壤N2O排放特征及关键影响因子。本研究利用静态暗箱-气相色谱法以“菜心(P1)-生菜(P2)-甜玉米(P3)-菜心(P4)”典型粮蔬轮作模式下农田土壤为研究对象进行周年原位观测(2022年11月22日 ~ 2023年12月3日)。试验设置5个处理,即仅施化肥处理(R)、商品有机肥替代15%化肥氮处理(M15%)、商品有机肥替代30%化肥氮处理(M30%)、尾菜堆肥替代15%化肥氮处理(S15%)和不施氮肥处理(CK)。结果表明:各有机肥替代处理的作物产量与R处理相比均无显著差异。整个观测期内各施氮处理N2O排放峰值一般在施肥伴随灌溉事件后2 ~ 6天内出现,各处理N2O排放通量介于2.85 ~ 2446.49 μg N2O m-2 h-1之间。R处理N2O周年排放总量分别为2.66 kg N hm-2,各有机肥替代处理比其增加了25.56% ~ 52.25%。R处理P1、P2、P3、P4生长季及休闲期N2O排放总量分别为0.22、0.30、1.24、0.35和0.55 kg N hm-2,分别占年排放总量的8.13%、11.37%、46.69%、13.31%和20.50%。对于N2O季节排放总量,P1和P2生长季各有机肥替代处理与R处理无显著差异,P3生长季高于R处理,P4生长季均显著低于R处理(P < 0.05)。N2O周年排放系数介于0.15% ~ 0.31%之间。随着土壤平均温度升高,N2O平均排放通量随之升高;CK处理土壤N2O排放通量与WFPS之间存在显著的负相关关系(P < 0.05);N2O排放峰出现时间与较高土壤NO3--N含量出现时间较一致。广东省粮蔬轮作模式下有机肥替代化肥氮措施增加了周年土壤N2O排放,而该措施对季节N2O排放总量的影响在不同作物生长季有所差异。氮肥施用、有机肥种类、土壤温度和湿度是影响土壤N2O排放的主要因子。

     

    Abstract: This study aims at exploring the nitrous oxide (N2O) emissions and key impact factors under alternative organic fertilizer substitution managements from Guangdong province, which has hot and rainy climate, acidic soils, and high multiple cropping index cultivation. We conducted one year in situ observations (from November 22, 2022, to December 3, 2023) by using the static opaque chamber method. Flowering Chinese cabbage (P1), lettuce (P2), sweet corn (P3) and flowering Chinese cabbage (P4) were cultivated in turn in this study. Five treatments were implemented: only chemical fertilizer application (R), substitution 15% and 30% of chemical fertilizer nitrogen with commercial organic fertilizer (M15% and M30%), substitution 15% of chemical fertilizer nitrogen with composted vegetable residue (S15%), and no nitrogen fertilizer application (CK). The results show there was no significant difference in crop yield between organic fertilizer replacement treatment and R treatment. During the whole observation period, the peak of N2O emission of each nitrogen application treatment generally occurred within 2 ~ 6 days after the irrigation event, and the N2O emission flux of each treatment ranged from 2.85 ~ 2446.49 μg N2O m-2 h-1. The annual N2O emission of R treatment was 2.66 kg N hm-2 , and the N2O emission of each organic fertilizer treatment increased by 25.56% ~ 52.25%. The total N2O emissions of P1, P2, P3, P4 were 0.22, 0.30, 1.24, 0.35 and 0.55 kg N hm-2, respectively, they accounted for 8.13%, 11.37%, 46.69%, 13.31% and 20.50% of the total annual emissions respectively. There was no significant difference between substituting organic manure for compound treatments and R treatment in seasonal emissions for P1 and P2. Seasonal emissions were higher in substituting organic manure for compound treatments than that in R treatment for P3, and which were lower for P4(P < 0.05). The annual N2O emission factors ranged from 0.15% to 0.31% . The mean N2O emission flux increased with the increase of soil temperature, and there was a significant negative correlation between N2O emission flux and WFPS (P < 0.05). N2O emission peak appeared with high soil NO3--N contents. Under patterns of grain and vegetable rotation in Guangdong province, organic fertilizer substitution managements increased annual N2O emissions, but they had different impacts on seasonal N2O emissions. Nitrogen fertilizer application, type of organic fertilizer, soil temperature and moisture were identified as primary factors influencing soil N2O emissions.

     

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