东亚地区春季一氧化碳的输送特征研究

以ECMWF ERA-40再分析资料构建的气象场为驱动场,利用全球三维大气化学模式MOZART-2,模拟了2001年3月大气污染物浓度的全球时空分布,并以一氧化碳(CO)作为示踪剂分析了春季东亚污染物向西太平洋地区输送的路线和机制.为了检验模拟结果的合理性,对TRACE-P 期间典型天气过程下的模拟结果与观测结果进行了比较.比较结果显示,模拟结果可以较好地再现2001年春季冷锋过境期间与东南亚深对流运动加强的天气形势下,东亚污染物向西太平洋地区输送的2大主要路径及其特征:(1) 污染物被冷锋系统提升后,在对流层中层向西太平洋快速传输;(2) 强烈的大气对流运动可以导致东南亚生物质燃烧产生的污染物在对流层上层向西太平洋输送.     

基于水声环境空间中多模态深度融合模型的目标识别方法研究

随着对水下目标特性研究的深入和声学探测技术的发展,基于单模态的阵列式信息融合或基于空间信息的分布式信息融合的水下目标识别方法研究已有一定成果,但针对复杂海况导致单一物理场或单一融合层次的系统识别性能提高有限等方面影响的水下目标识别方法研究还有所不足,因此,开展基于多模态深度融合模型的水下目标识别方法研究可利用模态互补,共享信息而提升识别率。文中在国内外研究基础上,深入研究了基于到达时差法和多模态方法组合的检测方法,初步形成了基于水声环境空间中多模态深度融合模型的识别框架,开展了海洋中典型自然与人为事件的信号分析与特征提取,并在此基础上,设计新型基于海底基站的被动识别系统。该系统同步记录和由位置等组成的时间序列标记声、磁和压数据,可实现高精度、高分辨率的识别。本研究可满足未来海洋观测对高性能水下目标探测、定位和跟踪系统的迫切需要,为海洋安全监管、海洋突发事件应急响应等领域提供新的技术手段和科学参考。     

Environmental impact of fluidized solidified silt casting on surrounding water bodies

Abstract

With the growing demand for underwater refill engineering, the construction technology of implementing fluidized solidification in underwater pouring has recently received increased attention. However, the environmental impact of underwater casting on surrounding water bodies, especially when the silt is polluted, is still unclear. In this study, a simulated underwater pouring test and a static immersion release test were conducted separately to study the quality of the surrounding water during and after pouring. The results showed that fluidized-solidified silt casting could increase the pH of the surrounding water, even after the pouring had stopped, by approximately 1.0 and the turbidity could reach 200 NTU. No diffusion of Zn and Cu into the surrounding water was observed and while Ni and Cr exhibited slight diffusion, this was at a level well below international water quality standard. During construction, reducing the distance from the seafloor to the bottom of the pouring catheter could reduce the level of pollution. After construction, the use of neutral solidified materials can effectively reduce the pH of the surrounding water and the potential risk of heavy metal dissolution.     

同步辐射标定平面镜反射率不确定度分析方法研究

为了提高多通道软X射线能谱仪的测量精度,2009年在北京同步辐射(BSRF)软X束线源上对多种材料的掠入射平面镜的反射率进行了标定.在标定实验的基础上,对光源的单色性、高次谐波以及源强稳定性、探测器响应一致性和数据采集统计误差等多项不确定因素进行了评估,给出了反射率的修正方法和相应的不确定度分析结果.     

极性分子型电流变液导电机理研究

极性分子型电流变液是一种新型的电流变材料.其介电颗粒上吸附极性分子,极性分子在颗粒间强局域电场作用下发生取向是产生巨电流变效应的关键.通过对Ca—Ti—O(CTO)体系极性分子型电流变液电流密度的测量发现,其导电行为遵从Poole-Frenkel效应的规律,这是极性分子型电流变液的重要特征之一.而500 ℃处理过的CTO粉体不含极性分子,所配制的电流变液无巨电流变效应,其电流密度随外电场强度近似地呈线性关系,显示出传统电流变液特性.     

不同结构林带防风效能风洞模拟

防风林带结构是影响防风效能的主要因素。建立不同宽度、不同株行距林带防风效能与林带后距离之间的统计模型,可以为防风林建设提供指导性意见。通过风洞实验,在11 m·s^-1风速下,对4种宽度、5种株行距林带的背风面0~10H（H为林带高度）的风速进行测定,采用曲线参数估计法、傅立叶模型、SSF模型（Sum of Sin Functions）,构建了不同结构林带防风效能与林带后距离间的统计模型。结果表明：傅立叶模型拟合不同宽度林带的防风效能与林带后距离的关系效果最优,可决系数（R²）均在98%以上;SSF模型拟合不同株行距林带的防风效能与林带后距离的关系效果最优（R²>0.98）。根据构建的统计模型,风速为11 m·s^-1左右时,林带宽度8 m（两行一带）的防风林的防风效能存在明显优势;5种株行距的林带中,株行距为8 m×8 m的防风林带本试验条件下防风效果最好。     

临沂市土地整理项目后期管护的做法

临沂市地处沂蒙山区,山区、丘陵、平原各占三分之一。近几年,临沂市政府高度重视土地开发整理工作,自2003年以来,共实施国家级项目17个、省级项目12个、市级项目177个、县级项目1130个,争取国家和省级资金5.3亿元,投入市、县级项目资金6.6亿多元,项目总规模9.8万hm^2,新增耕地2.2万余公顷,新建新修灌溉水渠347.89km,     

临沂市加强土地开发整理推动新农村建设

土地开发整理与新农村建设相结合,是当前社会关注的热点之一。临沂市高度重视通过土地整理促进新农村建设,自2003年以来,共实施国家和省、市、县四级土地开发整理项目1335个,累计投入11．12亿元,项目总规模14．4万hm^,新增耕地2．2万hm^2。通过实施土地开发整理,新建灌溉渠系1930km,排水沟2315km,新上泵站313个,农用井661眼,新上输变电线路287km,     

Urban three-dimensional expansion and its driving forces —A case study of Shanghai, China

Urban expansion is a phenomenon of urban space increase, and an important measuring index of the process of urbanization. Taking Shanghai as an example, the changes of urban average height and built-up area were studied to represent city’s vertical and horizontal increases respectively, and statistical methods were used to analyze the driving forces of urban expansion. The research drew following conclusions: 1) The urban expansion process of Shanghai from 1985 to 2006 had a clear periodic feature, and could be divided into three stages: vertical expansion in dominance, coordinated vertical and horizontal expansion, and horizontal expansion in dominance. 2) The average height and quantity of buildings in core city were significantly bigger than those in suburbs, but the changing speed of the latter was faster. And 3) urbanization process was the major driving force for the city’s horizontal expansion, while industrial structure improvement was the key driving factor for the vertical expansion. Those two driving forces were simultaneously affected by city’s political factors.