Research on N2O Emission Fluxes of 3 Cultivated Grasslands in Growing Seasons

doi:10.11733/j.issn.1007-0435.2015.04.006

Acta Agrestia Sinica ›› 2015, Vol. 23 ›› Issue (4): 703-709.DOI: 10.11733/j.issn.1007-0435.2015.04.006

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Research on N₂O Emission Fluxes of 3 Cultivated Grasslands in Growing Seasons

LI Yuan, WANG Tao, ZHOU Ying, YANG Qian, SHEN Yu-ying

State Key Laboratory of Grassland Agro-ecosystems, College of Pastoral Agriculture Science and Technology, Lanzhou University, Lanzhou, Gansu Province 730020, China

Received:2014-06-26 Revised:2014-08-28 Online:2015-08-15 Published:2015-08-26

3种栽培草地N₂O释放通量季节动态的研究

李渊, 王涛, 周莹, 杨倩, 沈禹颖

兰州大学草地农业科技学院草地农业生态系统国家重点实验室, 甘肃兰州 730020

通讯作者: 沈禹颖
作者简介:李渊(1990-),男,甘肃酒泉人,硕士研究生,研究方向为草类作物与环境,E-mail:liyuan13@lzu.edu.cn
基金资助:
教育部重大科技项目(313028);甘肃省重大科技专项(1203FKDA035);教育部创新团队(IRT13019)资助

Abstract

Abstract:

In order to determine the relationships between the N₂O emission fluxes of cultivated grassland in growing season and soil moisture, temperature, nitrate nitrogen content or ammonium nitrogen content, the N₂O emission fluxes of Kentucky bluegrass (Poa pratensis),lucerne (Medicago sativa) and sainfoin (Onobrychis viciaefolia) cultivated grasslands were observed during growing seasons in the Loess Plateau using a static chamber-HPLC method. The results showed that N₂O emission fluxes had significant difference in among 3 cultivated grasslands(P <0.05),Kentucky bluegrass grassland had the highest N₂O emission fluxes. The N₂O emission fluxes of Kentucky bluegrass, sainfoin and lucerne grassland were -0.3185~0.4943, -0.4962~0.4755, -0.3167~0.4620 mg·m^-2·h^-1, respectively. The N₂O accumulated emission fluxes of Kentucky bluegrass grasslands was obviously higher than those of lucerne and sainfoin. The N₂O emission fluxes of 3 cultivated grasslands reached the peak during florescence, while N₂O absorption was observed during regenerative phase. The N₂O emission fluxes of Kentucky bluegrass was mainly affected by soil moisture, and the N₂O emission fluxes of two legume cultivated grasslands were related with the contents of nitrate-N and ammonium-N.

Key words: Cultivated grassland, Arid area, Nitrous oxide, Emission fluxes

摘要：

为探究栽培草地生长季N₂O释放规律与其土壤水分、温度及土壤硝态氮、铵态氮含量的关系,在黄土高原旱塬区,采用静态箱-气相色谱法,研究早熟禾(Poa pratensis)、紫花苜蓿(Medicago sativa)和红豆草(Onobrychis viciaefolia)草地生长季N₂O释放通量季节动态。结果表明:3种栽培草地生长季N₂O释放通量差异显著(P <0.05)。早熟禾草地N₂O释放通量最高,红豆草草地次之,紫花苜蓿草地最小。通量变化范围分别为-0.3185~0.4943,-0.4962~0.4755,-0.3167~0.4620 mg·m^-2·h^-1。生长季内早熟禾草地N₂O累积释放通量显著高于紫花苜蓿和红豆草草地。3种栽培草地N₂O释放通量在花期出现峰值,在再生期出现吸收现象。早熟禾草地N₂O释放通量主要受土壤水分影响。2种豆科栽培草地N₂O释放通量主要与土壤硝态氮、铵态氮含量相关联。

关键词: 栽培草地, 旱地, 氧化亚氮, 释放通量

CLC Number:

X502

LI Yuan, WANG Tao, ZHOU Ying, YANG Qian, SHEN Yu-ying. Research on N₂O Emission Fluxes of 3 Cultivated Grasslands in Growing Seasons[J]. Acta Agrestia Sinica, 2015, 23(4): 703-709.

李渊, 王涛, 周莹, 杨倩, 沈禹颖. 3种栽培草地N₂O释放通量季节动态的研究[J]. 草地学报, 2015, 23(4): 703-709.

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References

[1] IPCC.Climate change 2001: the scientific basis[M]. Cambridge:Cambridge university press,2001
[2] Keeney D R. Nitrogen management for maximum efficiency and minimum pollution[J]. Nitrogen in Agricultural Soils,1982(2):605-649
[3] Bremner J M. Sources of nitrous oxide in soils[J]. Nutrient Cycling in Agroecosystems,1997,49(1/3):7-16
[4] Rochette P, Angers D A, Bélanger G, et al. Emissions of N₂O from Alfalfa and Soybean Crops in Eastern Canada[J]. Soil Science Society of America Journal,2004,68(2):493-506
[5] 熊正琴,邢光熹,鹤田治雄,等. 种植夏季豆科作物对旱地氧化亚氮排放贡献的研究[J]. 中国农业科学,2002,35(9):1104-1108
[6] Zhong Z, Lemke R L, Nelson L M. Nitrous oxide emissions associated with nitrogen fixation by grain legumes [J]. Soil Biology and Biochemistry,2009,41(11):2283-2291
[7] Bhandral R, Bittman S, Kowalenko C G, et al. Emissions of nitrous oxide after application of dairy slurry on bare soil and perennial grass in a maritime climate [J]. Canadian Journal of Soil Science,2008,88(4):517-527
[8] 卢琦. 荒漠化对全球气候变化的响应[J]. 中国人口资源与环境,2002,12(1):95-98
[9] 陈宝书. 牧草饲料作物栽培学[M]. 北京:中国农业出版社,2005:205-329
[10] 杨世琦,孙兆敏,杨雄年. 发展苜蓿草产业促进西北旱区农业结构调整[J]. 西北农业学报,2003,12(4):157-160
[11] Chapuis Lardy L, Wrage N, Metay A, et al. Soils, a sink for N₂O? A review [J]. Global Change Biology,2007,13(1):1-17
[12] 王涛,周莹,王先之,等. 黄土高原旱塬区陇东苜蓿草地N₂O释放动态及微生物驱动因子的研究[J]. 西北植物学报,2013,33(10): 2113-2119
[13] 史瑞和,鲍士旦,秦怀英. 土壤农化分析[M]. 第二版.北京:中国农业出版社,1996:30-67
[14] 李梓铭,杜睿,王亚玲,等. 中国草地N₂O通量日变化观测对比研究[J]. 中国环境科学,2013,32(12):2128-2133
[15] 于克伟,陈冠雄,杨思河. 几种旱地农作物在农田N₂O释放中的作用及环境因素的影响[J]. 应用生态学报,1995,6(4):387-391
[16] Bhandral R, Bittman S, Kowalenko C G, et al. Emissions of nitrous oxide after application of dairy slurry on bare soil and perennial grass in a maritime climate[J]. Canadian Journal of Soil Science,2008,88(4):517-527
[17] 章家恩,刘文高,陈景青,等. 刈割对牧草地下部根区土壤养分及土壤酶活性的影响[J]. 生态环境,2005,14(3):387-391
[18] 孙志高,刘景双,杨继松,等. 三江平原典型小叶章湿地土壤硝化、反硝化作用与氧化亚氮排放[J]. 应用生态学报,2007,18(1):185-192
[19] Xing G X, Zhu Z L. Preliminary studies on N₂O emission fluxes from upland soils and paddy soils in China[J]. Nutrient Cycling in Agroecosystems,1997,49(1/3):17-22
[20] 张光亚,陈美慈,闵航,等. 设施栽培土壤氧化亚氮释放及硝化,反硝化细菌数量的研究[J]. 植物营养与肥料学报,2002,8(2):239-243
[21] Kim D G, Giltrap D, Hernandez-Ramirez G. Background nitrous oxide emissions in agricultural and natural lands: a meta-analysis[J]. Plant and Soil,2013,373(1/2):17-30
[22] 曹心德,陈莹. 环境条件变化对土壤中稀土元素溶解释放的影响[J]. 中国环境科学,2000,20(6):486-490

Research on N₂O Emission Fluxes of 3 Cultivated Grasslands in Growing Seasons

3种栽培草地N₂O释放通量季节动态的研究

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