VSC-HVDC输电系统的特点与应用

轻型直流输电系统是基于VSC技术的新型直流输电技术。介绍轻型直流输电基本原理,对比轻型直流输电技术与传统直流输电技术在结构和功能方面的区别,阐述轻型直流输电的优点,并对其应用进行总结和展望,以期为轻型直流输电技术在我国的应用和发展提供一定参考。     

天然气发动机国Ⅴ排放技术研究

研究天然气发动机技术的发展,选取稀薄燃烧的技术路线。通过对电控量的标定和后处理的匹配,使单燃料天然气发动机排放达到国Ⅴ排放标准。     

中国水稻土酸化时空变化特征及其对氮素盈余的响应

针对水稻土酸化造成作物减产和严重污染环境的问题,收集了1979-1985年全国第二次土壤普查成果和2015-2017年水稻土质量等级调查成果,结合2005-2015年全国测土配方施肥数据,采用空间分析和统计分析方法,分析了1979-2017年,39年间中国水稻土pH值空间分布的变化;计算了39年间不同水稻土pH值分级和...     

基于SupReMe影像重建和RF的玉米冠层LAI反演

针对Sentinel-2卫星影像拥有3个对植被生长状况非常敏感、空间分辨率为20m的红边波段（705、740、783nm）,其空间分辨率与可见光和近红外波段10m的空间分辨率不一致,使Sentinel-2影像应用受到限制的问题,基于多光谱多分辨率估计的超分辨率（Super-resolution for multispectral multiresoltion estimation, SupReMe）算法将空间分辨率20m的6个波段重建为10m;以重建后的影像为数据源,耦合PROSAIL辐射传输模型和随机森林模型反演玉米冠层叶面积指数（LAI）,并以野外实测LAI验证其反演精度。结果表明,采用SupReMe算法对Sentinel-2影像进行重建后,在保持光谱特性不变的同时提高了影像的空间细节;基于重建影像和原始影像的LAI反演决定系数R2分别为0.70、0.68,均方根误差RSME分别为0.240、0.262。研究表明,利用SupReMe算法重建后的Sentinel-2卫星影像,能够在提高玉米冠层LAI反演空间分辨率的同时提高反演精度,在挖掘高分辨率农作物生长信息方面具有很大潜力。     

洱海湖滨区畜禽粪便污染与资源化利用措施

通过对洱海湖滨区畜禽生产及其粪便污染与利用现状进行调查研究,针对生产中存在的问题,提出控制污染加快畜禽粪便资源化利用措施。     

水稻耐低钾基因型的筛选及吸钾特性的研究

筛选水稻耐低钾基因型最直接、客观方法是在低钾土壤上进行田间实验直接筛选,其结果可作为其他方法的比较标准.但该方法需时较长、工作量大,不能满足大批量快速、高速筛选的要求.因此,近年来国内外许多学者在探索用液培的方法进行筛选[1,2].     

近57年中国北方气候干湿变化及与太平洋年代际振荡的关系

利用中国北方424个气象站点1960—2016年逐日地面观测资料,应用联合国粮农组织(FAO)Penman-Monteith模型计算潜在蒸散(ET0),基于降水量和潜在蒸散计算的湿润指数研究了1960—2016年中国北方干湿气候时空变化特征,分析了太平洋年代际振荡(PDO)对气候干湿变化的影响。结果表明:北方总体干湿变化不显著,空间上表现为西北、青藏高原、内蒙古湿润化而华北干旱化的特征。极端干旱区面积显著缩小,干旱区、半干旱区则明显扩张,表明气候敏感区域在扩张。极端干旱区和干旱区显著变湿润,半干旱区有变湿润的趋势。1960—1990年至1991—2016年,北方经历了变湿润的过程。西北西部、青藏高原湿润化趋势明显,极端干旱—干旱区的界线呈西界东移、南北界线收缩的变化。干旱化趋势主要发生在华北和东北部分地区,华北黄河沿线一带半干旱—半湿润区界线向东南方向扩张。东北中部和西北西部由于降水增加而ET0减少,气候变湿润。华北中西部、内蒙古东部和东北部分地区降水减少、ET0增加,气候变干旱。在PDO暖位相,西北、东北北部及内蒙古东部地区地表气候偏湿润;在PDO冷位相,地表气候偏干旱。而华北则相反。     

穴盘苗吹叶补苗机构设计与试验

针对叶片遮挡穴盘苗空穴机械补苗作业时存在损伤待补空穴周围穴盘苗叶片的问题,该研究提出一种使用射流气管吹开遮挡叶片进行机械补苗的吹叶补苗方法。作业时,射流气管内通高压气流,由待补空穴底端渗水孔向上移动,吹开遮挡叶片,到达穴盘苗叶片顶部后,补苗机械手夹持待补苗使基质块底部靠近射流气管顶端,并与射流气管同步下移完成补苗作业。吹叶机构射流气管内径5 mm,顶端封闭,靠近顶端的水平截面均布开设8个直径1.2 mm的射流孔。搭建由吹叶机构与挂接于Denso机械手臂的补苗机械手组成的试验装置,对72穴穴盘培育的红掌、白掌、芥蓝、菜心、白菜和生菜6种不同叶片遮挡程度的穴盘苗进行单穴吹叶补苗性能试验。结果表明,吹叶机构与补苗机械手协同作业的补苗成功率与穴盘苗初始叶片遮挡率（穴盘待补空穴被相邻穴盘苗叶片遮挡的面积与穴孔面积的比值）、遮挡叶片倾角和射流气管压力有关。在射流气管射流孔数为8,射流孔直径1.2 mm条件下,射流气管压力为0.28 MPa时,初始叶片遮挡率59.4%的红掌穴盘苗的补苗成功率可达92%;射流气管压力为0.22 MPa时,初始叶片遮挡率56.2%的白掌穴盘苗的补苗成功率可达94%;射流气管压力为0.22～0.31 MPa时,初始叶片遮挡率35.4%的芥蓝穴盘苗的补苗成功率均可达90%;射流气管压力为0.16～0.31 MPa时,初始叶片遮挡率29.7%～35.8%的菜心、白菜和生菜穴盘苗的补苗成功率均可达90%。研究结果可为叶片遮挡穴盘苗空穴的机械补苗设备开发提供技术参考。     

Identification and characterization of conjugated linolenic acid isomers by Ag+-HPLC and NMR

Interest in the biological activity of conjugated linolenic acids (CLnA) is growing. Technically, previous methods could not fully characterize and identify CLnA isomers. The present study is the first report on application of silver ion impregnated high-performance liquid chromatography (Ag+-HPLC) into separation of CLnA methyl ester (CLnAMe) mixture. Compared with the GC and reversed-phase HPLC techniques, Ag+-HPLC could resolve and separate CLnAMe isomers into three clusters of peaks namely ttt, ctt and ctc geometrical groups. Each positional isomer belonging to the same geometrical group could be further separated by Ag+-HPLC. Quantitative 13C NMR properties of CLnAMe mixture were subsequently studied. Olefinic signals in the CLnAMe mixture were assigned and used to quantify each isomer in combination with Ag+-HPLC. The present study provided a detailed analysis of a complex CLnA mixture and may have an important application in future studies dealing with synthesis, oxidative stability, and bioactivity of individual CLnA isomers.     

Biodegradation of 1-Methylindole and 3-Methylindole by Mangrove Sediment Enrichment Cultures and a Pure Culture of an Isolated Pseudomonas Aeruginosa Gs

Indolic compounds are N-heterocyclic aromatic chemicals and have been detected at contaminated sites. Biodegradation of 1-methylindole (1MI) and 3-methylindole (3MI) was investigated initially using enrichment cultures with mangrove sediment obtained from Mai Po Nature Reserve of Hong Kong and subsequently with a pure culture of Pseudomonas aeruginosa Gs confirmed with 16S rRNA gene. At 2.0 mM, 1MI and 3MI were degraded in 4 and 3 days, respectively, by the respective 1MI- and 3MI-degrading enrichment cultures. When substrate concentrations were increased to 3.0,mM and 3.5,mM, slower degradation of 1MI and 3MI was observed indicating inhibitory effects from the substrates, possibly due to toxicity. In addition, no colony of bacteria could be observed on the agar plates amended with 3.5,mM 1MI or 4.0,mM 3MI, indicating that 1MI was more toxic than 3MI. Pseudomonas aeruginosa Gs, isolated from the enrichment culture, effectively utilized both substrates as the sole source of carbon and energy. Complete degradation of 1MI and 3MI was achieved after more than 40 days and 24 days, respectively, at an initial concentration of 2,mM in the culture. Effects of initial substrate concentration, pH and salinity on degradation of 1MI and 3MI by P. aeruginosa Gs were also studied in batch culture. The optimum pH and salinity for degrading both substrates by P. aeruginosa Gs was 7.0 and 5?, respectively. Biodegradation kinetics of 1MI and 3MI by P. aeruginosa Gs could be described using a first-order kinetic model. Our results suggest that both 1MI and 3MI are biodegradable in the mangrove environment and that toxicity of 1MI could be a potential factor limiting the removal of the chemical in the environment by microorganisms.