首页 | 本学科首页   官方微博 | 高级检索  
相似文献
 共查询到19条相似文献,搜索用时 531 毫秒
1.
稻田甲烷排放及产生、转化、输送机理   总被引:65,自引:1,他引:64  
王明星  李晶  郑循华 《大气科学》1998,22(4):600-612
通过对中国五大水稻产区稻田甲烷排放的多年观测实验,描述了稻田甲烷排放的时空变化规律及特征并分析研究了其形成机理。稻田甲烷排放的日变化有四种类型,甲烷的传输效率是日变化形成的主要因素。稻田甲烷土壤中排放率的季节变化型式在不同的地区是不同的,这取决于气温变化、水稻品种、施肥及水管理等不同因素。甲烷产生主要发生在稻田土壤耕作还原层(2~20 cm),氧化主要发生在水土交界面的氧化层和根部氧化膜,并受多种因子的影响。土壤中的甲烷通过三个路径向大气排放,不同时期三个路径在甲烷传输中的相对重要性不同。施用化肥和沼渣肥可以降低土壤中甲烷的产生和排放,而有机肥会增加土壤中甲烷的产生和排放。中国的稻田每年向大气中排放9.67~12.66百万吨甲烷,全球稻田甲烷的总排放量约为35~56 Tg/a。  相似文献   

2.
通过对长春及其周围地区稻田上空甲烷浓度和稻田甲烷排放量持续2年的监测研究发现,在水稻生长季内,该区稻田甲烷排放量的变化曲线里单峰型,排放高峰出现在7月上、中旬至8月上旬的水稻孕穗期,且在此期间,稻田上空甲烷浓度和稻田甲烷排放量关系密切。采用持续淹水方式的C稻田的甲烷平均排放通量为7.65mg·m-2·h-1;采用间歇灌水方式的A、B稻田分别为0.Z7和0.72mg·m-2·h-1。人为的水管理方式和施肥对该区稻田甲烷排放具有重要影响。采用间歇灌水的水管理方式可大幅度降低稻田甲烷的排放量。  相似文献   

3.
对甲烷湿地排放模型CH4MODwetland进行灵敏度分析表明,环境驱动因素——温度和地表水深是影响甲烷排放通量的主要因素,地表水深对季节性积水沼泽甲烷排放通量的灵敏度大于常年积水沼泽。模型对植物和土壤输入参数的灵敏度响应依次为Wmax(地上生物量最大值)FR(地下净初级生产力占植物总净初级生产力的比例)fV(植被类型系数)TAmax(植物从生长初期到最大地上生物量所需有效积温)ρ(容量),OM(土壤有积质含量)SAND(土壤砂粒含量)。以经验水位模型驱动CH4MODwetland,模拟三江平原毛果苔草和小叶章沼泽(1950年代~2000年代),以及若尔盖高原木里苔草和乌拉苔草沼泽(1960年代~2000年代)多年甲烷排放通量的变化。结果表明,年代际甲烷排放通量的变化主要受降水量的影响,但气候变暖使得降水量基本相同的年代甲烷排放通量增加:三江平原毛果苔草沼泽和小叶章沼泽(1980年代~2000年代比1950年代~1970年代模拟的甲烷排放通量分别增加了9.5%和8.3%;若尔盖高原乌拉苔草沼泽和木里苔草沼泽(1990年代~2000年代比1960年代~1970年代)分别增加了6.0%和5.5%。该结论能够为评估未来气候变化对中国湿地甲烷排放的影响提供依据。  相似文献   

4.
主要介绍了近 2 0年来稻田甲烷排放的模式研究和排放量的估算以及减少稻田甲烷排放的措施。数值模式是估算稻田甲烷排放量的一条有效途径 ,模式的研究现在正处于发展阶段。介绍了几个主要的模型 ,既有物理过程模型也有经验模型。年排放量的估算范围为 6 79~ 4 1 4Tg ,随着技术的发展和大量实验的进行估算值的精度正得到不断的提高。减排措施是减少稻田甲烷排放的必要手段 ,但是目前的减排技术均处于研究阶段 ,应用还不成熟  相似文献   

5.
应用初步建立的全球二维大气化学模式,对工业革命以来甲烷的长期变化进行了模拟研究。模式将CH4、CO和NOx排放源方案进行了参数化。在考虑了CH4排放源以及对OH浓度有重要影响的CO和NOx排放源的长期变化的基础上,模拟了CH4和OH浓度自1840年到20世纪90年代的长期变化趋势。结果表明,工业革命前的大气甲烷体积分数和年排放总量分别为760×10-9和280Tg,1991年大气甲烷的体积分数和年排放总量分别为1611.9×10-9和533.9Tg。而对流层中OH的数密度则由1840年的7.17×105cm-3变化到1991年的5.79×105cm-3,下降了19%。如果CH4、CO及NOx这三种排放源继续按给定的方案增长,那么到2020年大气甲烷的体积分数和年排放总量将增加为2090.7×10-9和966.2Tg,而OH的数密度将为5.47×105cm-3,比1840年降低24%。  相似文献   

6.
废弃物处理温室气体排放的主要排放源之一为废水(生活污水和工业废水)处理CH4排放。根据统计资料和IPCC提供的方法,选择适合中国的排放因子,分析了中国废水处理2005-2010年的CH4排放特征和2000-2010年CH4产生的各驱动因子。并且根据中国的实际情况预测和分析了中国废水处理CH4排放趋势和排放潜力。结果显示:2010年中国生活污水处理CH4排放量为61.10万t,工业废水处理的CH4排放量为162.37万t,造纸等八大行业CH4排放量达到总CH4排放量的92%以上,2005-2010年的CH4排放量逐年增加;到2020年在减排情景下,生活污水处理CH4排放量为101.36万t,减排潜力为7.63万t,比2010年排放量增加了66%;工业废水处理CH4排放量233.93万t,减排潜力为25.99万t,比2010年排放量增加了44%。  相似文献   

7.
江西省冬水田休闲期甲烷排放研究   总被引:2,自引:0,他引:2       下载免费PDF全文
利用85个气象站的观测资料和14个农业气象观测站水稻生育期资料,以及第二次土壤普查数据,基于气温与冬水田休闲期甲烷排放通量的指数关系模型,分析了江西省2000—2013年冬水田休闲期甲烷排放因子和排放量的时空分布特征。结果表明:1)江西省冬水田甲烷排放因子无显著的上升趋势;2)江西省冬水田休闲期甲烷排放平均通量为7.66 mg/(m2·h),平均年排放因子为406.5 kg/hm2,其中2007年排放通量为1.214×105 t,占稻田甲烷排放的12.4%;3)吉安、赣州、抚州、上饶和宜春市是江西省冬水田休闲期甲烷排放的主要地区,累计约占全省排放量的75.0%;4)各设区市冬水田休闲期甲烷排放量主要决定于各地水田面积的大小,赣州市除外。  相似文献   

8.
基于EOF和小波分析的福建近40年旱涝时空变化特征研究   总被引:9,自引:3,他引:9  
采用经验正交函数分解(EOF)、快速富里叶变换(FFT)、连续(CWT)和正交小波变换(OWT),对近41a来福建省25个代表站不同雨季旱涝指数(Z指数)序列进行了分析。结果表明:(1)福建旱涝在1965—1975年及1990年代具有显著的2-3a周期;(2)在1980年代中期以后南北反向变化具有显著的1a和3-4a周期;(3)中西部与其它区域的反向变化,在1985—1998年间有显著的1-2a周期,在1980年代以后9-13a周期较强;(4)近40年来有干旱趋势,南部(东部)比北部(西部)明显,其中1990年代这种趋势显著。(5)1960年代和1980年代相对湿润,而1970年代和1990年代则相对干旱。  相似文献   

9.
我国杭州地区秋和稻田的甲烷排放   总被引:10,自引:1,他引:10  
1987年秋季在杭州郊区采用一套全自动的观测系统,对稻田的甲烷排放进行了观测。在整个晚稻灌溉期内,稻田是大气甲烷的一个源地,其甲烷释放率最高可达240mg/m~2·h。甲烷释放率具有很强的季节性变化,在水稻成熟期之前,甲烷释放率一般在40-60mg·CH_4/m~2·h的水平上波动,在成熟期间则降为10mg·CH_4/m~2·h的水平。除移栽期外的整个水稻生长期间的甲烷平均释放率为39mg/m~2·h。甲烷释放率具有明显的日变化,一般在午夜至凌晨3—4点达最大值,白天较低,变化也较小。这可能与水稻植物体由于其生理上的日变化引起的甲烷气体传输能力的日变化有关。实验没有观测到不同施肥(K_2SO_4和菜饼)对甲烷释放率的明显影响。阴雨天的降温一般在2—3天后引起甲烷释放率的迅速下降,这可能是因土壤中发酵细菌如产甲烷菌数量的减少造成的。尽管甲烷释放率和土壤温度在整个生长期间基本上是逐步下降的,但两者之间并没有简单的正相关性。土壤中产生的甲烷气体只有一小部分释放到大气中,从土壤中冒出来的气泡往往可引起释放率的急剧上升。1985年全球稻田的甲烷释放量估计为134±3lTg(1Tg=10~(12)g),其中12±26Tg和30±6Tg分别来自亚太地区和中国稻田。  相似文献   

10.
农田生态系统温室气体排放研究进展   总被引:39,自引:0,他引:39  
自1985年起,中国科学院大气物理研究所利用自行设计制造的自动观测仪器系统,历时十六年先后对我国四大类主要水稻产区的甲烷排放规律及其与土壤、气象条件和农业管理措施的关系进行了系统野外观测实验,并对稻田甲烷产生、转化和输送机理进行了理论研究,探讨了控制稻田甲烷排放的实用措施,建立了估算和预测稻田甲烷排放的数值模型.在甲烷排放的时空变化规律和转化率研究方面有一系列新的发现,在稻田甲烷产生率、排放率及其与环境条件的关系方面取得一系列新的成果,以充分证据改变了国际上关于全球和中国稻田甲烷排放总量的估算.在对稻田甲  相似文献   

11.
1990年7—9月,在浙江临安(30°14'N,119°42'E),利用微气象学(梯度廓线)法及箱式技术对水稻田CH4排放通量进行了同步观测,取得了中稻整个生长期内的CH4排放资料。文章仅对箱式技术的观测结果作了介绍与分析。观测发现在整个灌溉期内,稻田CH4释放率为3.67—16.14 mg/m2·h,均值为10.58 mg/m2·h。CH4排放的季节变化明显,日变化也同样很明显。另外还发现,CH4排放通量与水(地)温及其他气象因素,如强风、阴雨等有关。与梯度廓线法的观测结果不同,箱式观测到的CH4排放通  相似文献   

12.
减少温室气体排放以减缓全球变暖是当前全球变化研究的主要关注点。制定区域适应性的减排措施,有赖于对不同环境条件下温室气体排放空间差异性的进一步研究。广东是我国主要的双季稻种植区,其气候条件及稻田耕作方式都有别于我国其他稻区的。为估算广东省区域稻甲烷(CH_4)排放情况,利用IPCC2006清单指南中的稻田甲烷模型——CH_4MOD,模拟计算了2010年广东省21个地市双季早(晚)稻CH_4排放量及其排放因子。结果显示:1) 2010年稻田CH_4排放量为60. 74万t,其中双季晚稻CH_4排放量35. 01万t,双季早稻CH_4排放量25. 73万t。2)稻田CH_4排放量空间分布不均,区域稻田甲烷排放量为粤西的粤北的珠江三角洲的粤东的,排放量分别为21. 22万t、17. 02万t、15. 14万t、7. 36万t。3)双季早稻CH_4排放因子明显小于晚稻的,双季早稻CH_4排放因子为261. 18 kg CH_4/hm~2,双季晚稻为358. 53 kg CH_4/hm~2。4)空间上,粤西地区稻田CH_4排放因子水平较高,粤北、粤东的处于中等水平,珠江三角洲稻田CH_4排放水平最低。  相似文献   

13.
成都平原稻田甲烷排放的实验研究   总被引:9,自引:0,他引:9  
根据1996~1999年四个稻季的观测资料,分析了成都平原单季稻甲烷排放的季节变化和年际变化特征.结果表明:在水稻生长季节甲烷排放通量变化很大,在分蘖期和成熟期一般会出现峰值.年际间的通量变化也很大,其年均排放通量的变化范围在2.35~33.95mg m-2 h-1之间.4年的平均排放通量为12 mg m-2 h-1,与四川乐山的7年平均值30mg m-2 h-1相比,存在着明显的地区差异.同时分析讨论了温度、施肥、水稻品种、土壤氧化还原电位(Eh)以及稻田水位等诸多因素对稻田甲烷排放的影响.结果表明:在成都平原水稻生长季节的平均气温对CH4的平均排放通量影响不大;而气温对CH4排放的日变化有相对重要的影响,但气温对甲烷排放日变化的影响与水稻植物体的生长阶段有关;发现了水稻植物体(根、茎、叶)重量对CH4排放的重要作用.讨论了合理使用肥料和施肥量,控制水位和Eh值对稻田CH4的减排作用,提出优化组合诸影响因子,以充分发挥其减排潜力.  相似文献   

14.
A global data set on the geographic distribution and seasonality of freshwater wetlands and rice paddies has been compiled, comprising information at a spatial resolution of 2.5° by latitude and 5° by longitude. Global coverage of these wetlands total 5.7×106 km2 and 1.3×106 km2, respectively. Natural wetlands have been grouped into six categories following common terminology, i.e. bog, fen, swamp, marsh, floodplain, and shallow lake. Net primary productivity (NPP) of natural wetlands is estimated to be in the range of 4–9×1015 g dry matter per year. Rice paddies have an NPP of about 1.4×1015 g y–1. Extrapolation of measured CH4 emissions in individual ecosystems lead to global methane emission estimates of 40–160 Teragram (1 Tg=1012 g) from natural wetlands and 60–140 Tg from rice paddies per year. The mean emission of 170–200 Tg may come in about equal proportions from natural wetlands and paddies. Major source regions are located in the subtropics between 20 and 30° N, the tropics between 0 and 10° S, and the temperate-boreal region between 50 and 70° N. Emissions are highly seasonal, maximizing during summer in both hemispheres. The wide range of possible CH4 emissions shows the large uncertainties associated with the extrapolation of measured flux rates to global scale. More investigations into ecophysiological principals of methane emissions is warranted to arrive at better source estimates.  相似文献   

15.
To understand methane (CH4) and nitrous oxide (N2O) emissions from permanently flooded rice paddy fields and to develop mitigation options, a field experiment was conducted in situ for two years (from late 2002 to early 2005) in three rice-based cultivation systems, which are a permanently flooded rice field cultivated with a single time and followed by a non-rice season (PF), a rice-wheat rotation system (RW) and a rice-rapeseed rotation system (RR) in a hilly area in Southwest China. The results showed that the total CH4 emissions from PF were 646.3±52.1 and 215.0±45.4 kg CH4 hm-2 during the rice-growing period and non-rice period, respectively. Both values were much lower than many previous reports from similar regions in Southwest China. The CH4 emissions in the rice-growing season were more intensive in PF, as compared to RW and RR. Only 33% of the total annual CH4 emission in PF occurred in the non-rice season, though the duration of this season is two times longer than the rice season. The annual mean N2O flux in PF was 4.5±0.6 kg N2O hm-2 yr-1. The N2O emission in the rice-growing season was also more intensive than in the non-rice season, with only 16% of the total annual emission occurring in the non-rice season. The amounts of N2O emission in PF were ignorable compared to the CH4 emission in terms of the global warming potential (GWP). Changing PF to RW or RR not only eliminated CH4 emissions in the non-rice season, but also substantially reduced the CH4 emission during the following rice-growing period (ca. 58%, P<0.05). However, this change in cultivation system substantially increased N2O emissions, especially in the non-rice season, by a factor of 3.7 to 4.5. On the 100-year horizon, the integrated GWP of total annual CH4 and N2O emissions satisfies PF>>RR≈RW. The GWP of PF is higher than that of RW and RR by a factor of 2.6 and 2.7, respectively. Of the total GWP of CH4 and N2O emissions, CH4 emission contributed to 93%, 65% and 59% in PF, RW and RR, respectively. These results suggest that changing PF to RW and RR can substantially reduce not only CH4 emission but also the total GWP of the CH4 and N2O emissions.  相似文献   

16.
Methane emission from rice paddies   总被引:3,自引:0,他引:3  
Methane release rates from rice paddies have been measured in Andalusia, Spain, during almost a complete vegetation period in 1982 using the static box system. The release rates ranged between 2 and 14 mg/m2/h and exhibited a strong seasonal variation with low values during the tillering stage and shortly before harvest, while maximum values were observed at the end of the flowering stage. The CH4 release rate, averaged over the complete vegetation period, accounted for 4 mg/m2/h which results in a worldwide CH4 emission from rice paddies of 35–59×1012 g/yr if we assume that the observed CH4 release rates are representative of global conditions. The CH4 release rates showed diurnal variations with higher values late in the afternoon which were most likely caused by temperature variations within the upper layers of the paddy soils. Approximately 95% of the CH4 emitted into the atmosphere by rice paddies was due to transport through the rice plants. Transport by bubbles or diffusion through the paddy water was of minor importance. Incubation experiments showed that CH4 was neither produced nor consumed in the paddy water. The relase of CH4 from rice paddies caused a diurnal variation of CH4 in ambient air within the rice-growing area with maximum values of up to 2.3 ppmv during the early morning, compared to average daytime values of 1.75 ppmv.  相似文献   

17.
旋转正压大气中的非线性Schrödinger方程和大气阻塞   总被引:1,自引:0,他引:1       下载免费PDF全文
本文利用WKB方法导出了旋转正压大气中的非线性Rossby波所满足的立方Schrödinger方程,指出在1≤m≤2的情况下,非线性Schrödinger方程具有包络孤立波解,同时我们还对大气中的包络Rossby孤立波的流场进行了计算,结果得到了阻塞高压和切断低压等结构,并且这些阻塞系统能够维持五天以上。  相似文献   

18.
Summary The CH4 emission rates from Chinese rice fields have been measured in five typical areas representing all of the five major rice culture regions in People's Republic of China (P.R. China). Four types of diurnal variations (afternoon peak, night peak, afternoon-night double peaks and random pattern) of CH4 emission rates have been found. The first pattern was normally found in clear weather, the second and the third types were only found occasionally in particular place, while the fourth were found in cloudy or rainy weather. Due to the irregular pattern of the methane production observed in the morning-afternoon comparison experiment, the transport pathway influenced by certain factors, may be the major factor governing the diurnal variation of CH4 emission. Seasonal variation patterns of CH4 emission differ slightly with different field locations, where climate system, cropping system and other factors are different. Two and three emission peaks were generally found during single and early rice vegetation periods, with the peak magnitude and time of appearance differing to small degree in individual sites. A decreasing trend of seasonal variation was always observed in late rice season. A combination of seasonal change of transport efficiency and that of CH4 production rate in the paddy soil explains well the CH4 emission. The role of rice plant in transporting CH4 varied over a large range in different rice growing stages. The reasons for internnual changes of CH4 flux are not yet clear.Great spatial variation of the CH4 emission has been found, which can be attributed to the differences in soil type and soil properties, local climate condition, rice species, fertilizer and water treatment. Experiments showed that while the application of some mineral fertilizers will reduce the CH4 emission and CH4 production in the soil, the application of organic manure will enhance CH4 emission and CH4 production in the soil. Any measures which can get off easily decomposed carbon from organic manure may reduce C supply for CH4 production, and hence reduce CH4 emission. Fermented sludges from biogas generators and farmyard-stored manure seem to be promising. In some parts of China, separate application of the organic and mineral manure instead of mixed application could be another option. Frequent Scientific drainage and ridge cultivation, which are often used water management techniques in Chinese rice agriculture, have been proved in the experiments to be a very efficient mitigation measures to reduce CH4 emission from rice fields.By summarizing the present available data, China's rice fields contribute about 13.3 Tg yr–1 (11.4–15.2) CH4 to the atmosphere. The total methane emission from global rice fields can be estimated 33–60 Tg yr–1, much less than the estimates made before.If we extrapolate the measured data in China with a consideration of measured data in other Asian country, the total global emission of CH4 from rice fields are estimated to be about 35–60 Tg yr–1 With 2 Figures  相似文献   

19.
There is growing concern that increasing concentrations of greenhouse gases in the atmosphere have been responsible for global warming through their effect on radiation balance and temperature. The magnitude of emissions and the relative importance of different sources vary widely, regionally and locally. The Indus Basin of Pakistan is the food basket of the country and agricultural activities are vulnerable to the effects of global warming due to accelerated emissions of GHGs. Many developments have taken place in the agricultural sector of Pakistan in recent decades in the background of the changing role of the government and the encouragement of the private sector for investment in new ventures. These interventions have considerable GHG emission potential. Unfortunately, no published information is currently available on GHG concentrations in the Indus Basin to assess their magnitude and emission trends. The present study is an attempt to estimate GHG (CO2, CH4 and N2O) emissions arising from different agro-ecosystems of Indus Basin. The GHGs were estimated mostly using the IPCC Guidelines and data from the published literature. The results showed that CH4 emissions were the highest (4.126 Tg yr^-1) followed by N20 (0.265 Tg yr^-1) and CO2 (52.6 Tg yr^-1). The sources of CH4 are enteric fermentation, rice cultivation and cultivation of other crops. N2O is formed by microbial denitrification of NO3 produced from applied fertilizer-N on cropped soils or by mineralization of native organic matter on fallow soils. CO2 is formed by the burning of plant residue and by soil respiration due to the decomposition of soil organic matter.  相似文献   

设为首页 | 免责声明 | 关于勤云 | 加入收藏

Copyright©北京勤云科技发展有限公司  京ICP备09084417号