淹水稻田甲烷产生和排放的研究现状

大气中温室气体如ＣＯ２、ＣＨ４和Ｎ２Ｏ等增加，导致全球气候变暖。ＣＨ４虽浓度相对较低，但其捕获热量的效率却比ＣＯ２高２０－３０倍，并以每年１％的速度增加，本文阐述了淹水稻田ＣＨ４排放过程及数量，稻田土壤类型，栽培措施对ＣＨ４产生与排放的影响，ＣＨ４排放与水稻生长关系。同时讨论了控制和缓解稻田ＣＨ４排放的途径。     

水分状况对水田土壤N2O排放的影响

通过室内培养试验,研究了不同水分含量下水稻土的Ｎ２Ｏ排放,结果表明,在水分含量相当于田间持水量时,土壤具有最大的Ｎ２Ｏ排放速率,当水分含量在田间持水量之上时,反硝化作用是Ｎ２Ｏ的主要来源。水分含量在田间持水量之下时,尽管硝倾作用强烈,但Ｎ２Ｏ排放量较小。通过温室盆栽试验研究了不同水分管理措施下,水稻土Ｎ２Ｏ和ＣＨ４的排放,同常规水分管理方式相比,长期淹水显著增加ＣＨ４的排放而减少了Ｎ２Ｏ的排放。相反,湿润灌溉的处理在整个水稻生长期内没有明显的ＣＨ４排放,但其Ｎ２Ｏ排放对水分状况敏感,出现数次峰值,从而总排放量远高于其它两处理。     

农业微环境对土壤温室气体排放的影响

二氧化碳（ＣＯ２）、氧化氮（Ｎ２Ｏ）、甲烷（ＣＨ４）等气体排放量的增加所引进的温室效应是全球变暖的主要促动因素。同时各种温室气体的产生和排放量也同样受其所处环境状况的影响与反馈作用研究各环境要素对土壤温室气体排放的主要影响机制是调节气候变化与温室气体排放循环反馈过程的关键环节,对减少温室气体排放、减缓全球变暖真挚具有较强的现实意义。阐述了土壤排放Ｎ２０、ＣＨ４对环境因素的影响,并提出温室气体减排措     

土壤水分状况对CH4氧化,N2O和CO2排放的影响

实验室培育试验表明，土壤氧化ＣＨ４，排放Ｎ２Ｏ和ＣＯ２的最佳水分含不量。水稻土氧化ＣＨ４的最佳水分含同于半干旱草地土壤，均接近于土壤环境常年水分含量。水稻土Ｎ２Ｏ排放量随着水分含量的下降而增加，半干旱草地土壤则随着水分含量的下降而减少，表明背离土壤环境上水分含量越远，Ｎ２Ｏ的排放量越大。因而，ＣＨ４氧化和Ｎ２Ｏ排放对土壤水分含量的反应呈极显著的负相关性。ＣＯ２排放的最佳水分含量接近或高于ＣＨ４氧化     

温室气体与土壤

云、水蒸汽，ＣＯ２，ＣＨ４，Ｎ２Ｏ，Ｏ３等大气中的主要成分（温室气体）可减少从地表逸出的红外辐射的损失，而使地球表面大体保持恒温（温室效应）。当氯氟轻，ＣＨ４，Ｎ２Ｏ的浓度增大，可破坏平流层中的Ｏ３，使较多的紫外辐射到达到表，危害活细胞并引起地球变暖（增强温室效应）。平流层中的Ｏ３经反应可形成激发态氧原子，与Ｈ２Ｏ，ＣＨ４，Ｎ２Ｏ分子反应产生具有活性的ＮＯ，ＯＨ及ＣＨ３自由基，它们可氧化由地球逸出     

土壤水分状况和质地对稻田N2O 排放的影响

１９９４年中国科学院封丘生态试验站通过小区试验研究了土壤质地和水分状况对稻田Ｎ２Ｏ排放的影响。结果表明稻田Ｎ２Ｏ排放主要受土壤水分状况的影响,淹水状态下,Ｎ２Ｏ排放很少,水分落于期间Ｎ２Ｏ排放量占水稻生长期Ｎ２Ｏ排放总量的８７．５０％～９８．６５％。土壤质地显影响稻田平均Ｎ２Ｏ排放通量,砂质土壤排放的Ｎ２Ｏ显或极显高于壤质和粘质土壤,水稻生长期砂质、壤质及粘质土壤的平均Ｎ２Ｏ排放通量分别为１３７．６３、８７．５４和６３．６μｇＮ２Ｏ－Ｎ／ｍ＾２．ｈ。     

温室气体及其生态效应

研究分析了ＣＯ２、ＣＨ４、Ｎ２Ｏ、ＳＯ２、ＣＦＣｓ等主要温室气体的生态效应,结果表明其生态效应与其性质及浓度有关,提出了缓解温室气体释放的有效对策。     

土壤Eh和温度对稻田甲烷排放季节变化的影响

通过温室盆栽试验研究了土壤Ｅｈ和温度对稻田甲烷（ＣＨ４）排放季节变化时影响。结果表明,当水稻生长期土壤Ｅｈ处于适宜ＣＨ４产生的水平时,土壤Ｅｈ对ＣＨ４排放季节变化没有显著影响,这时土壤温度却显著影响ＣＨ４排放季节变化。土壤Ｅｈ的季节变化与ＣＨ４排放季节变化间存在显著相关性,而土壤温度却没有。     

中国农业响应全球气候变化的策略问题

本文对“中国农业响应全球气候变化的策略问题”进行了探讨和研究，指出在保证我国经济增长和社会发展的同时，努力减少温室气体排放和保护生态环境昌我们的基本原则，在此基础上探讨了提高农业产量增强对气候变化的适应能力、农业减排温室气体（二氧化碳ＣＯ２，甲烷ＣＨ４，氧化亚氮Ｎ２Ｏ）的各项对策措施，以及争取国际资金援助及技术转让的必要性等具体问题。     

对我国控制农业源温室气体排放的建议——借鉴几个发达国家的做法

农业部门排放ＣＨ４、ＮＯｘ等温室气体，是引起全球变暖的原因之一。本文通过介绍几个发达国家控制农业源温室气体排放措施，提出对我国农业源温室气体减排的措施建议。     

Emissions of CO2, CH4 and N2O from Southern European peatlands

Peatlands play an important role in emissions of the greenhouse gases CO₂, CH₄ and N₂O, which are produced during mineralization of the peat organic matter. To examine the influence of soil type (fen, bog soil) and environmental factors (temperature, groundwater level), emission of CO₂, CH₄ and N₂O and soil temperature and groundwater level were measured weekly or biweekly in loco over a one-year period at four sites located in Ljubljana Marsh, Slovenia using the static chamber technique. The study involved two fen and two bog soils differing in organic carbon and nitrogen content, pH, bulk density, water holding capacity and groundwater level. The lowest CO₂ fluxes occurred during the winter, fluxes of N₂O were highest during summer and early spring (February, March) and fluxes of CH₄ were highest during autumn. The temporal variation in CO₂ fluxes could be explained by seasonal temperature variations, whereas CH₄ and N₂O fluxes could be correlated to groundwater level and soil carbon content. The experimental sites were net sources of measured greenhouse gases except for the drained bog site, which was a net sink of CH₄. The mean fluxes of CO₂ ranged between 139 mg m⁻² h⁻¹ in the undrained bog and 206 mg m⁻² h⁻¹ in the drained fen; mean fluxes of CH₄ were between −0.04 mg m⁻² h⁻¹ in the drained bog and 0.05 mg m⁻² h⁻¹ in the drained fen; and mean fluxes of N₂O were between 0.43 mg m⁻² h⁻¹ in the drained fen and 1.03 mg m⁻² h⁻¹ in the drained bog. These results indicate that the examined peatlands emit similar amounts of CO₂ and CH₄ to peatlands in Central and Northern Europe and significantly higher amounts of N₂O.     

Fluxes of CO2, CH4 and N2O from drained organic soils in deciduous forests

We examined net greenhouse gas exchange at the soil surface in deciduous forests on soils with high organic contents. Fluxes of CO₂, CH₄ and N₂O were measured using dark static chambers for two consecutive years in three different forest types; (i) a drained and medium productivity site dominated by birch, (ii) a drained and highly productive site dominated by alder and (iii) an undrained and highly productive site dominated by alder. Although the drained sites had shallow mean groundwater tables (15 and 18 cm, respectively) their average annual rates of forest floor CO₂ release were almost twice as high compared to the undrained site (1.9±0.4 and 1.7±0.3, compared to 1.0±0.2 kg CO₂ m⁻² yr⁻¹). The average annual CH₄ emission was almost 10 times larger at the undrained site (7.6±3.1 compared to 0.9±0.5 g CH₄ m⁻² yr⁻¹ for the two drained sites). The average annual N₂O emissions at the undrained site (0.1±0.05 g N₂O m⁻² yr⁻¹) were lower than at the drained sites, and the emissions were almost five times higher at the drained alder site than at the drained birch site (0.9±0.35 compared to 0.2±0.11 g N₂O m⁻² yr⁻¹). The temporal variation in forest floor CO₂ release could be explained to a large extent by differences in groundwater table and air temperature, but little of the variation in the CH₄ and N₂O fluxes could be explained by these variables. The measured soil variables were only significant to explain for the within-site spatial variation in CH₄ and N₂O fluxes at the undrained swamp, and dark forest floor CO₂ release was not explained by these variables at any site. The between-site spatial variation was attributed to variations in drainage, groundwater level position, productivity and tree species for all three gases. The results indicate that N₂O emissions are of greater importance for the net greenhouse gas exchange at deciduous drained forest sites than at coniferous drained forest sites.     

Effects of elevated atmospheric CO2, prolonged summer drought and temperature increase on N2O and CH4 fluxes in a temperate heathland

In temperate regions, climate change is predicted to increase annual mean temperature and intensify the duration and frequency of summer droughts, which together with elevated atmospheric carbon dioxide (CO₂) concentrations, may affect the exchange of nitrous oxide (N₂O) and methane (CH₄) between terrestrial ecosystems and the atmosphere. We report results from the CLIMAITE experiment, where the effects of these three climate change parameters were investigated solely and in all combinations in a temperate heathland. Field measurements of N₂O and CH₄ fluxes took place 1-2 years after the climate change manipulations were initiated. The soil was generally a net sink for atmospheric CH₄. Elevated temperature (T) increased the CH₄ uptake by on average 10 μg C m⁻² h⁻¹, corresponding to a rise in the uptake rate of about 20%. However, during winter elevated CO₂ (CO₂) reduced the CH₄ uptake, which outweighed the positive effect of warming when analyzed across the study period. Emissions of N₂O were generally low (<10 μg N m⁻² h⁻¹). As single experimental factors, elevated CO₂, temperature and summer drought (D) had no major effect on the N₂O fluxes, but the combination of CO₂ and warming (TCO₂) stimulated N₂O emission, whereas the N₂O emission ceased when CO₂ was combined with drought (DCO₂). We suggest that these N₂O responses are related to increased rhizodeposition under elevated CO₂ combined with increased and reduced nitrogen turnover rates caused by warming and drought, respectively. The N₂O flux in the multifactor treatment TDCO₂ was not different from the ambient control treatment. Overall, our study suggests that in the future, CH₄ uptake may increase slightly, while N₂O emission will remain unchanged in temperate ecosystems on well-aerated soils. However, we propose that continued exposure to altered climate could potentially change the greenhouse gas flux pattern in the investigated heathland.     

Greenhouse gas emissions and mitigation measures in Chinese agroecosystems

Globally, CO₂, CH₄ and N₂O, contribute 60%, 15% and 5%, respectively, to the anthropogenic greenhouse effect. Atmospheric CO₂, CH₄ and N₂O are currently increasing by 0.5%, 1.1% and 0.3% per year, respectively. This paper reviews studies on greenhouse gas emission and mitigation measures in China in recent years. CH₄ emissions originate mainly from rice paddy fields, and are determined by soil characteristics, e.g., temperature, water content, pH and Eh conditions, and by land and crop management, e.g., land use, rice varieties and fertilizer application. Rice paddies emit N₂O in addition to CH₄, however, the N₂O and CH₄ emission patterns are quite different. Fertilization practices and field water conditions are major factors that control N₂O emissions. In order to minimize net greenhouse gas emissions from agricultural production systems, either sources of emissions must be reduced, or agricultural greenhouse gas sinks must be enhanced or newly created. Because the effects of greenhouse gas mitigation measures on each greenhouse gas are different, specific practices must be developed and adopted for the various gases. This paper discusses some promising greenhouse gas mitigation strategies to reduce net emissions from agroecosystems in China.     

意大利中部地区粘土稻田干湿交替减少CH4排放但诱发N2O排放高峰

Reducing CH₄ and N₂O emissions from rice cropping systems while sustaining production levels with less water requires a better understanding of the key processes involved. Alternate wetting and drying (AWD) irrigation is one promising practice that has been shown to reduce CH₄ emissions. However, little is known about the impact of this practice on N₂O emissions, in particular under Mediterranean climate. To close this knowledge gap, we assessed how AWD influenced grain yield, fluxes and annual budgets of CH₄ and N₂O emissions, and global warming potential (GWP) in Italian rice systems over a 2-year period. Overall, a larger GWP was observed under AWD, as a result of high N₂O emissions which offset reductions in CH₄ emissions. In the first year, with 70% water reduction, the yields were reduced by 33%, CH₄ emissions decreased by 97%,while N₂O emissions increased by more than 5-foldunder AWD as compared to PF;in the second year, with a 40% watersaving,the reductions of rice yields and CH₄ emissions (13% and 11%, respectively) were not significant, but N₂O fluxes more than doubled. The transition from anaerobic to aerobic soil conditions resulted in the highest N₂O fluxes under AWD. The duration of flooding, transition to aerobic conditions, water levelabove the soil surface, and the relative timing between fertilization and flooding were the main drivers affecting greenhouse gas mitigation potential under AWD and should be carefully planned through site-specific management options.     

Emission of CO2, CH4 and N2O from lakeshore soils in an Antarctic dry valley

We measured soil profile concentrations and emission of CO₂, CH₄ and N₂O from soils along a lakeshore in Garwood Valley, Antarctica, to assess the extent and biogeochemical significance of biogenic gas emission to C and N cycling processes. Simultaneous emission of all three gases from the same site indicated that aerobic and anaerobic processes occurred in different layers or different parts of each soil profile. The day and location of high gas concentrations in the soil profile corresponded to those having high gas emission, but the pattern of concentration with depth in the soil profile was not consistent across sites. That the highest gas concentrations were not always in the deepest soil layer suggests either limited production or gas diffusion in the deeper layers. Emission of CO₂ was as high as 47 μmol m⁻² min⁻¹ and was strongly related to soil temperature. Soil respiration differed significantly according to location on the lakeshore, suggesting that factors other than environmental variables, such as the amount and availability of O₂ and nutrients, play an important role in C mineralization processes in these soils. High surface emission (maximum: 15 μmol m⁻² min⁻¹) and profile gas concentration (maximum: 5780 μL L⁻¹) of CH₄ were at levels comparable to those in resource-rich temperate ecosystems, indicating an active indigenous population of methanogenic organisms. Emission of N₂O was low and highly variable, but the presence of this gas and NO₃ in some of the soils suggest that denitrification and nitrification occur there. No significant relationships between N₂O emission and environmental variables were found. It appears that considerable C and N turnover occurs in the lakeshore soils, and accurate accounting will require measurements of aerobic and anaerobic mineralization. The production and emission of biogenic gases confirm the importance of these soils as hotspots of biological activity in the dry valleys and probable reservoirs of biological diversity.     

Soil organic matter: Distribution,genesis, and management to reduce greenhouse gas emissions

In this paper we describe the accumulation of soil organic matter (SOM) during pedogenesis and the processes that can lead to the emission of greenhouse gases (CO₂, CH₄, N₂O) to the atmosphere via SOM decomposition and denitrification. We discuss the role of management on SOM accumulation and loss, and the potential for controlling emission or comsumption of greenhouse gases by soils. We conclude that under current climate conditions there are global scale opportunities to reduce greenhouse gas emissions from soils and increase the indirect sequestration of greenhouse gases in soils through improved soil management.     

Net fluxes of CO2, but not N2O or CH4, are affected following agronomic-scale additions of urea to prairie and arable soils

While experimental addition of nitrogen (N) tends to enhance soil fluxes of carbon dioxide (CO₂), methane (CH₄), and nitrous oxide (N₂O), it is not known if lower and agronomic-scale additions of urea-N applied also enhance trace gas fluxes, particularly for semi-arid agricultural lands in the northern plains. We aimed to test if this were true at agronomic rates [low (11 kg N ha⁻¹), moderate (56 kg N ha⁻¹), and high (112 kg N ha⁻¹)] for central North Dakota arable and prairie soils using intact soil cores to minimize disturbance and simulate field conditions. Additions of urea to cores incubated at 21 °C and 57% water-filled pore space enhanced fluxes of CO₂ but not CH₄ and N₂O. At low, moderate, and high urea-N, CO₂ fluxes were significantly greater than control but not fluxes of CH₄ and N₂O. The increases in CO₂ emission with rate of urea-N application indicate that agronomic-scale N inputs may stimulate microbial carbon cycling in these soils, and that the contribution of CO₂ to net greenhouse gas source strength following fertilization of semi-arid agroecosystems may at times be greater than contributions by N₂O and CH₄.     

不同耕作条件下豆麦双序列轮作农田土壤温室气体的排放及影响因素研究

为了研究耕作措施对双序列轮作农田土壤温室气体的排放及影响, 采用CO₂分析仪、静态箱 气相色谱法在陇中黄土高原半干旱区对传统耕作不覆盖、免耕不覆盖、免耕秸秆覆盖和传统耕作+秸秆还田4种耕作措施下豆麦双序列轮作农田土壤温室气体(CO₂、N₂O和CH₄)的排放及影响因素进行了连续测定和分析。结果表明: 测定期内4种耕作措施下农田土壤均表现为CO₂源、N₂O源和CH₄净吸收汇; 除传统耕作不覆盖措施, 其他3种耕作措施不同程度地减少了2种轮作序列土壤的N₂O排放通量, 并显著增加了土壤对CH4的吸收。CO₂和N₂O的排放通量分别与地表、地下5 cm处、地下10 cm处的土壤温度呈极显著和显著正相关关系, 相关系数分别为0.92^**和0.89^**、0.95^**和0.91^**、0.77^*和0.62^*; 而CH₄吸收通量与不同地层的温度之间无明显的相关关系; CO₂和CH₄的通量与0~5 cm、5~10 cm的土壤含水量均呈显著正相关关系, 相关系数分别为0.69^*和0.72^*、0.77^*和0.64^*, 而与10~30 cm土壤含水量无明显相关关系; N₂O排放通量与各层次的土壤含水量之间均呈不显著负相关关系。对2种轮作序列各处理下土壤中排放的3种温室气体的增温潜势计算综合得出: 4种耕作措施中, 免耕不覆盖处理可相对减少土壤温室气体的排放量, 进而降低温室效应。     

Effect of plant-mediated oxygen supply and drainage on greenhouse gas emission from a tropical peatland in Central Kalimantan,Indonesia

Abstract

To evaluate the hypothesis that plant-mediated oxygen supplies decrease methane (CH₄) production and total global warming potential (GWP) in a tropical peatland, the authors compared the fluxes and dissolved concentrations of greenhouse gases [GHGs; CH₄, carbon dioxide (CO₂) and nitrous oxide (N₂O)] and dissolved oxygen (DO) at multiple peatland ecosystems in Central Kalimantan, Indonesia. Study ecosystems included tropical peat swamp forest and degraded peatland areas that were burned and/or drained during the rainy season. CH₄ fluxes were significantly influenced by land use and drainage, which were highest in the flooded burnt sites (5.75 ± 6.66 mg C m^?2 h^?1) followed by the flooded forest sites (1.37 ± 2.03 mg C m^?2 h^?1), the drained burnt site (0.220 ± 0.143 mg C m^?2 h^?1), and the drained forest site (0.0084 ± 0.0321 mg C m^?2 h^?1). Dissolved CH₄ concentrations were also significantly affected by land use and drainage, which were highest in the flooded burnt sites (124 ± 84 μmol L^?1) followed by the drained burnt site (45.2 ± 29.8 μmol L^?1), the flooded forest sites (1.15 ± 1.38 μmol L^?1) and the drained forest site (0.860 ± 0.819 μmol L^?1). DO concentrations were influenced by land use only, which were significantly higher in the forest sites (6.9 ± 5.6 μmol L^?1) compared to the burnt sites (4.0 ± 2.9 μmol L^?1). These results suggest that CH₄ produced in the peat might be oxidized by plant-mediated oxygen supply in the forest sites. CO₂ fluxes were significantly higher in the drained forest site (340 ± 250 mg C m^?2 h^?1 with a water table level of ?20 to ?60 cm) than in the drained burnt site (108 ± 115 mg C m^?2 h^?1 with a water table level of ?15 to +10 cm). Dissolved CO₂ concentrations were 0.6–3.5 mmol L^?1, also highest in the drained forest site. These results suggested enhanced CO₂ emission by aerobic peat decomposition and plant respiration in the drained forest site. N₂O fluxes ranged from ?2.4 to ?8.7 μg N m^?2 h^?1 in the flooded sites and from 3.4 to 8.1 μg N m^?2 h^?1 in the drained sites. The negative N₂O fluxes might be caused by N₂O consumption by denitrification under flooded conditions. Dissolved N₂O concentrations were 0.005–0.22 μmol L^?1 but occurred at < 0.01 μmol L^?1 in most cases. GWP was mainly determined by CO₂ flux, with the highest levels in the drained forest site. Despite having almost the same CO₂ flux, GWP in the flooded burnt sites was 20% higher than that in the flooded forest sites due to the large CH₄ emission (not significant). N₂O fluxes made little contribution to GWP.