1988-2018年滇池氮磷比的时空演变特征与原因解析

氮、磷浓度是制约湖泊营养状态和生产力水平的重要环境因子,而氮磷化学计量比是湖泊生态系统的主要指标,因此,判识氮磷比变化趋势及其驱动力对湖泊生态恢复具有重要意义.研究基于19882018年连续观测数据,分析了滇池氮磷浓度和氮磷摩尔比(简称氮磷比)的时空分布演变特征;采用多元线性回归模型分别对滇池草海和外海氮磷比驱动效应进行定量解析,筛选出影响湖体氮磷比变化的潜在驱动因子.结果表明:①19882018年滇池氮磷比呈现显著的线性上升趋势,其中草海和外海氮磷比分别上升1.3和0.7 a^-1.②草海和外海分别在2008年和2004年发生了氮磷比上升突变,突变前上升归因于总氮浓度快速增加,突变后则是由于总磷浓度下降较快.③滇池的氮磷浓度变化主要是受流域氮磷输入负荷、跨流域调水、流域氮磷削减、风速和水位的综合影响,但受控因子在不同区域可能存在差异.④气温是滇池氮磷比变化的主要驱动因子,流域人为氮磷输入差异是滇池氮磷比变化的次要驱动因子.     

Study on the multi-sources of ore-forming materials and ore-forming fluids in the Huize lead-zinc ore deposit

TheHuizelarge sizedPb ZndepositinYunnan ProvinceislocatedinthecenteroftheSichuan Yun nan GuizhouPb Zn Agpolymetalmineralizationzone(SYGPb ZnMMD)inwesternYangtzePlateandis oneofthefamousPb Zn GebasesinChina(Wang Jiangzhenetal.,2003;WangXiaochunetal.,2000).Thisdeposit,whichischaracterizedbylarge scale(Pb+Znmetallicreservesarehigherthan5mil liontons),highPb+Zngrade(thePb+Zngradesof mostoresare25%-35%),highabundanceofuseful associatedelements(Ag,Ge,Cd,Ga,etc.)and someimportantbreakt…     

The rotation of 53 Be stars

Through spectral observations we obtained the rotational velocity Vsini for 53 Be stars, and estimated the values of V and i on the basis of Hutching's method. We analysed the effect of rotation on the width of emission lines and used the emission peak separation to determine the relative size of the shell and the photosphere and the dilution factor. We discuss in depth fast rotating models where stellar winds are present and their relation to the Be phenomenon.     

甘肃漳县王家店组孢子组合及其时代

本文首次报道甘肃漳县大草滩王家店组发现的丰富的化石孢子研究结果。在王家店组除孢子外,还发现少量疑源类(Acritarchs)和虫颚化石(Scole-codonts)。本文图示14个孢子属,23种和变种(包括未定种),根据孢子在地层中分布规律和演化特征,自下而上可划分为两个孢子带,下带称Retispora lepido-phyta-Knoxisporites literatus(LL)带,上带称Retispora lepidophyta-Hymenozonotrletes explanatus(LE)带。 甘肃漳县大草滩王家店组孢子带可以与华南和西藏珠穆朗玛峰地区的孢子带比较,同时可与西欧(Clayton et al,Higgs et al. ,1987)晚泥盆世晚期的Retis-pora lepidophyta-Knoxisporites literatus(LL)带和Retispora lepidophyta-Hymenozonotriletes explanatus(LE)带比较,时代为晚泥盆世晚期斯特隆阶(Strunian)早中期。     

Study on the Late PermianClaraia in South China

There are different opinions on whetherClaraia appeared in the Late Permian or not. It is convinced thatClaraia had turned up in the Late Permian through the study on the Upper Permian in South China.Pseudoclaraia, Claraioides andClaraia are compared and they are found to bear basically the same features. According to the rule of nomenclatural priority,Pseudoclaraia andClaraioides should be attributed to the genusClaraia. Late PermianClaraia lived in the middle-lower part of the bathyal continental slope as epifauna, which could swim occasionally. The study onClaraia of the Permian-Triassic transition shows that TriassicClaraia was evolved from PermianClaraia.     

陕西神府矿区束鸡沟流域风蚀水蚀交互作用特征研究

以神府矿区束鸡沟为典型小流域,讨论了风蚀水蚀交互作用的时空分布及其特征。风蚀水蚀交互作用在沙质坡面,坡面切沟和沙质沟道区表现最为突出,并形成了风蚀水蚀交互作用特有的侵蚀形态。     

三维结线动力无穷元及其特性研究

研究了文献[2]提出的结线动力无穷元的特性及其参数确定。由于这种单元将衰减函数定义在无穷向结线上,从而不仅可同时考虑多种波动形式,而且对于不同介质,不必通过改变节点坐标分布的形式实现介质间的过渡,而直接以结线上参数的改变来实现,因而可以更好地模拟无穷波动场,使用起来更方便．更容易推广。     

海南岛东南部新村港和黎安港潮汐特征及潮汐汊道P-A关系

以2013年8月实测的水位和流速资料为依据, 基于调和分析和统计方法分析了海南岛东南部新村港和黎安港潟湖的潮汐和潮流特征及其分布规律, 并探讨了潮汐汊道的P-A关系及其影响因素。结果表明, 双湖附近海域潮汐以全日分潮O1和K1为主, 半日分潮M2次之, 浅水分潮亦较显著, 属于非正规的全日混合潮; 调和常数反演的潮位与实测潮位基本吻合, 表明潟湖水位主要受潮汐控制。此外, 双湖均存在潮高日不等和涨落潮历时不等的现象, 涨潮历时略大于落潮历时。新村港平均高潮位0.65m, 较黎安港高0.15m; 平均低潮位-0.28m, 较黎安港低0.06m。新村港平均潮差0.50m, 最大可能潮差1.63m; 黎安港平均潮差0.36m, 最大可能潮差1.22m; 双湖平均潮差相差0.14m, 而最大可能潮差相差较大, 约0.41m。新村港平均潮差由口门向湾内有增大的趋势, 而黎安港却恰好相反。实测和模拟结果显示新村港和黎安港潟湖潮流分布格局类似, 都呈现出口门流速较大, 潟湖内部区域流速较小(小于0.1m/s)的分布规律, 且落潮流略强于涨潮流。新村港和黎安港的P-A值与华南海岸潮汐汊道P-A关系回归线吻合较好, 其中黎安港P-A值基本在华南海岸P-A关系回归线上, 而新村港略微有点偏离, 这说明新村港和黎安港潮汐汊道基本处于均衡状态。     

Rocky desertification poverty in Southwest China: Progress,challenges and enlightenment to rural revitalization

Journal of Geographical Sciences - Rocky desertification poverty (RDP) refers to rural poverty triggered or exacerbated by rocky desertification, which deprives farmers of opportunities for...     

Application of Arbuscular Mycorrhizal Inocula Might Be A Promising Method in the Restoration of Severely Degraded Wetlands

The application of arbuscular mycorrhizal (AM) inocula in severely degraded wetlands could ensure success in restoration.Mycorrhizal fungi play an important role in plant individual’s survival and development in a low nutrient condition.Based on the importance that mycorrhizal fungi have to their host plants,mycorrhizal inocula have been produced and applied in terrestrial ecosystems in order to let the plants become mycorrhizal.However,mycorrhizal inocula have not been used in wetland restorations,despite increasing evidence that mycorrhizal fungi are commonly found in various wetland systems and have the ability to survive under anoxic conditions.Evidence also shows that mycorrhizal fungal inocula in the soil could have been destroyed in the degraded wetland or could be destroyed during traditional wetland restoration process.Therefore,AM inocula production is strongly recommended for wetland restoration.In this paper,I will argue that AM inocula production is required when introduced recovery is necessary,and aeroponic culture technique is a preferable method to produce AM inocula.Last,a renewed wetland restoration flow chart is summarized.