我国小城镇可持续发展的体制性障碍及其对策探讨

以小城镇为载体的农村城镇化是我国城镇化进程的重要途径。小城镇可持续发展是我国社会经济可持续发展战略中的重要组成成部分。本文从当前小城镇可持续发展中存在的问题入手。深入分析了小城镇可持续发展的种种体制性障碍：行政等级化的城镇管理制度限制小城镇的公平发展；小城镇政府行政管理体制不健全；土地制度设置的不完善；阻碍了土地聚集和人口聚集的同步进行；小城镇基础设施建设缺少必要金融的支持；小城镇发展规划体制存在较大缺陷，并有针对性地提出了相应的体制改革对策与措施。     

中国可持续社会养老保险的综合评价体系和实证分析

我国可持续社会养老保险的综合评价指标体系包括四个层次和三级子系统，内容涉及养老保险人数、机构设置、基金管理和代际平衡四个子目标。应用因子分析模糊综合评价方法对我国1990-2001年养老保险建设状况进行评价，本文认为基金管理，行政管理和代际失衡是影响我国可持续养老保险发展的主要因素。     

贫困地区可持续发展指标体系及其综合评估--以湖南湘西贫困地区为例

本文依据贫困地区可持续发展固有的制约因素，特殊的内涵与目标，首次利用压力（Pressure)——状态（State)——响应（Respons)模型，构建了贫困地区可持续发展指标体系，并采用专家咨询与定量模型相结合的方法，对湖南湘西贫困地区可持续发展水平作了实证评估与分析。     

环境-经济系统整合模型的构建研究

环境经济系统整合模型的研究将环境的、经济的、社会的因素整合在可持续发展框架中．模拟、分析经济系统与环境系统之闻的相互作用和反馈关系。本文在分析环境经济系统整合模型构建的背景、理论与方法的基础上．设计了环境经济系统整合模型开发的技术路线．提出了环境经济系统整合模型的主要内容。     

基于复杂系统建模的水管理政策研究进展

基于Agent的建模方法（ABSS）通过自下而上的方式，考察系统中主体的不同状态和行为特征、主体与环境的作用、主体之间的作用，来表征系统的宏观特征，是进行复杂社会环境系统分析和政策研究的重要手段，在水资源、水环境管理系统中得到了有效的应用。本文在大量文献调研的基础上，讨论了ABSS建模方法的基本原理、主要特征、系统构成、分类方法和开发工具等特征，总结了其供水系统发展、水资源分配和流域水资源管理、农业土地和水资源利用、居民用水行为、农业污染控制及人类活动的水环境影响等方面的应用，分析了其在研究内容、研究方法、研究结果等方面的发展趋势，讨论了利用该方法研究我国水资源管理和水污染控制政策的必要性和重要性。     

Population Ageing and Sustainable Development Research in China

According to the United Nations population projections, the population of the elderly is expected to roughly triple in China from 2000 to 2050, particularly when the generations who were born between the 1950s and 1970s move through the age structure, and also because people are living longer and fertility rates have fallen, population aging is expected to put pressure on government's fiscal balance through higher old-age security benefits and health-care expenditures. This work draws together the broad range of elements involved within a consistent framework, based on a computable dynamic general equilibrium model with an overlapping generation structure. Further analysis using model simulation illustrates that the alternative schemes for the benefit rate, retirement age and technological progress are likely to be beneficial, and that an obvious slow-down in the growth of living standards is likely to be avoided.     

菌株qy37的异养硝化/好氧反硝化机制比较及氨氮加速降解特性研究

筛选出1株耐盐异养硝化-好氧反硝化菌qy37,通过形态观察、生理生化试验和16S rDNA序列分析,确定其为假单胞菌属(Pseudomonas).研究了异养硝化-好氧反硝化菌qy37的脱氮特性.在以NH4Cl为氮源的异养硝化系统内,该菌32 h内使NH 4+-N由138.52 mg/L降至7.88 mg/L,COD由2 408.39 mg/L降至1 177.49 mg/L,NH2 OH最大积累量为9.42 mg/L,NO 2--N最大积累量仅为0.02 mg/L,推测该菌将NH2OH直接转化为N2O和N2从系统中脱除.在以NaNO2为氮源的好氧反硝化系统内,该菌24 h内使NO 2--N由109.25 mg/L降至2.59 mg/L,NH2OH最大积累量为3.28 mg/L.好氧反硝化系统与异养硝化系统相比菌体生长量高,TN去除率低,COD消耗量低,NH2OH积累量低,并且检测到NO 3--N的积累.认为好氧反硝化在菌体生长和能量利用方面比异养硝化更有效率.在异养硝化-好氧反硝化混合系统内,16 h NH 4+-N去除速率比异养硝化系统提高了37.31%.混合系统的NH2 OH积累量低于异养硝化系统和好氧反硝化系统,但N2 O产出量高于二者.     

基于分形理论的江苏沿江城镇体系研究

开放条件下,“全球 地方”作用深刻影响着区域城镇体系,沿江发达地区表现尤其典型。基于分形的相关理论和方法,以2006年为时空断面,对江苏沿江地区城镇体系的空间分布进行实证研究。结果表明：（1）区域城镇规模等级结构服从Zipf定律,首位城市南京在区域城市体系中的垄断性相对较强,但并非处于绝对垄断地位;（2）空间关联维数显示,沿江地区城镇体系的交通网络通达性优良,各城镇间联系紧密;（3）根据分维数和无标度区分析,三大城市群中,宁镇扬城市群分形发育最好,苏锡常次之,通泰城市群分形发育最差;（4）扬州、镇江、南京和苏州的城镇集聚程度较高,分形发育较为成熟;南通、泰州、无锡和常州的集聚程度均较低,分形结构不佳。扬州在区域城镇体系中分形发育最为完善,中心性最好,历史上形成的这种空间格局至今没有变化.     

Dynamic Tracking and Comprehensive Evaluation on the Natural Resources Security Elements and System in China

System theory,pressure-state-response and drivingpressure-state-impact-response model have been applied to establishing China's dynamic tracking evaluation system of natural resources security in this article.Based on analytic hierarchy process and Delphi methods,the natural resources security situation has been evaluated systematically from 1991 to 2007.The result showed that the overall level of China's natural resources security presented a downtrend from 1991 to 2007.The basic reasons are the pressure indicators such as population,GDP,natural resources trade increased gradually,resulting in tension and fragility of natural resources security.     

Negotiation System of Ecological Compensation of Water Source Areas

In view of no generally accepted ecological compensation standards and methods at present,this paper discusses the introduction of the negotiation system to the process of ecological compensation for water source areas.That is,the government in water source areas and the downstream regions of river basins should confirm their respective rights and obligations and then establish their compensation standards through negotiations according to the different purposes of water use.The amount of compensation should be determined in the comprehensive consideration of the quality,quantity and compensation price of water.Through open and fair negotiations,an institutional arrangement will be set up,which can make the water source areas and the downstream regions of river basins fully express their true preferences and their independent choices on the ecological environment.