旅游发展背景下乡村适应性演化理论框架与实证

乡村转型及适应演化路径是乡村可持续发展领域重要研究内容,对实施乡村振兴战略及其多元目标的实现具有重要理论和现实意义。通过国家制度（战略）变迁关键时间节点,梳理典型案例乡村发展阶段,明确案例乡村转型适应的体制演化特征。在乡村适应性演化理论分析框架构建基础上,以体制转换明显的乡村为实证案例,结合农户调查与深度访谈数据,评估乡村适应演化下系统适应能力（结果）及农户生计响应效果,并基于归纳法和灰色关联分析,揭示乡村体制转换与微观农户生计关联的适应演化路径及机制。研究结果表明:（1）传统农业体制乡村向旅游体制转换后出现乡村经济发展和环境破坏、社会矛盾风险并存局面,农户生计适应选择对乡村转型响应呈现多样化。（2）不同适应路径农户生计恢复力存在显著差异,升级型、扩张型生计恢复力相对较高,维持型和更替型较低。（3）乡村体制转换（R₁到R_n）与农户生计适应（P₁到P₅）呈现协同且分化的演化路径,基础设施、政策扶持以及生态环境因子是乡村转型与农户生计关联适应演化的关键影响变量。     

张家界城镇居民幸福水平对旅游城镇化集聚的响应识别及测度

以欠发达地区城镇居民幸福水平对旅游城镇化集聚的响应为研究目标,构建二者的响应模型,识别和测度了城镇居民幸福水平对旅游城镇化集聚的响应强度。结果表明:（1）通过对张家界旅游城镇化集聚水平与城镇居民幸福水平进行格兰杰因果检验发现:旅游城镇化集聚是城镇居民幸福水平的单向格兰杰因果关系,即旅游城镇化集聚对城镇居民幸福水平具有正向促进作用。（2）由于受旅游城镇化集聚水平的影响,幸福水平在不同时期也受不同幸福外在因素的影响,关联度从精神文化环境、自然生态环境等非经济因素向社会安全环境、生活质量环境等经济因素转变。（3）旅游城镇化集聚对城镇居民幸福水平的作用路径区别于满足人们物质需求后,再满足非物质需求的传统幸福水平提升路径,而是先被动地改善“非物质”需求后继而带动“物质”需求改善以提升幸福水平。研究成果可为同类欠发达地区通过发展旅游城镇化提升居民幸福水平提供理论支撑及借鉴。     

温度和含水率对村镇垃圾焚烧烟气中有机物排放的影响

使用管式炉模拟村镇生活垃圾焚烧过程,研究不同焚烧温度和不同垃圾含水率条件下,村镇垃圾焚烧烟气中多环芳烃（PAHs）、氯苯及苯系物的生成和分布特性.结果表明,焚烧温度为550℃时,烟气中多环芳烃和氯苯的释放量最大,当温度小于550℃时,多环芳烃和氯苯的释放量随温度升高而增加,温度大于550℃时,多环芳烃和氯苯的释放量随温度升高而降低.高温焚烧不仅可以抑制烟气中多环芳烃的浓度及减少大分子量PAHs的排放,还能降低氯苯的释放量和氯代数,从而减小村镇垃圾焚烧烟气中的毒性;苯系物随着温度升高,由热解转变为高温合成,释放量也随着增加.水分对多环芳烃和氯苯有较大影响,对苯系物的影响较小.在400℃条件焚烧时,水分含量对多环芳烃总体上是促进的,而在850℃焚烧条件下则表现出抑制作用;而水分对氯苯则均表现出抑制作用,并且可以降低氯苯化合物的氯代数.     

我国能源资源税改革对城乡居民的收入分配效应——基于CGE模型的分析

通过构建包含7个城镇居民组和5个农村居民组的多收入阶层CGE模型,并将劳动力要素分为农业劳动力、技术工人和生产工人3类,在低税率、实际税率和高税率三种情景下模拟了煤炭、石油和天然气资源税改革单独实施和同时实施对城镇和农村居民的收入分配效应,并对税收补偿措施的效果进行分析.结果表明：单独实施煤炭资源税或天然气资源税改革对城镇居民组收入差距有正向的缩小作用,有利于收入分配公平,但对农村居民组收入差距起到负向的扩大作用,不利于收入分配公平;单独实施石油资源税改革则同时缩小了城镇和居民组的收入差距,有利于收入分配公平;同时实施三类能源资源税改革的收入分配效应与税率组合方式有关;将能源资源税收入以补贴的方式返还给农村居民可以缩小其收入差距,有利于收入分配公平.     

Analysing the sensitivity behaviour of two hydrology models

Recently, the New Morris Method has been presented as an effective sensitivity analysis tool for mathematical models. The New Morris Method estimates the sensitivity of an output parameter to a given set of input parameters (first-order effects) and the extent these parameters interact with each other (second-order effects). This method requires the specification of two parameters (runs and resolution) that control the sampling of the output parameter to determine its sensitivity to various inputs. The criteria for these parameters have been set on the analysis of a well-behaved analytical function (see Cropp and Braddock, Reliab. Eng. Syst. Saf. 78:77–83, 2002), which may not be applicable to other physical models that describe complex processes. This paper will investigate the appropriateness of the criteria from (Cropp and Braddock, 2002) and hence the effectiveness of the New Morris Method to determine the sensitivity behaviour of two hydrologic models: the Soil Erosion and Deposition System and Griffith University Representation of Urban Hydrology. In the first case, this paper will separately analyse the sensitivity of an output parameter on a set of input parameters (first- and second-order effects) for each model and discuss the physical meaning of these sensitivities. This will be followed by an investigation into the sampling criteria by exploring the convergence of the sensitivity behaviour for each model as the sampling of the parameter space is increased. By comparing these trends to the convergence behaviour from Cropp and Braddock (2002), we will determine how well the New Morris Method estimates the sensitivity for each model and whether the sampling criteria are appropriate for these models. It will be shown that the New Morris Method can provide additional insight into the functioning of these models, and that, under a different metric, the sensitivity behaviour of these models does converge confirming the sampling criteria set by Cropp and Braddock.     

“十四五”农村环境质量监测体系研究

介绍了国内外农村环境质量监测的发展历程和现状,总结了现行农村环境质量监测体系在体制机制、技术体系、应用支撑和数据共享等方面存在的主要问题,分析了"十四五"期间农村环境质量监测面临的挑战和机遇,指出"十四五"是农村生态环境保护的关键期、攻坚期和窗口期。根据环境管理对农业农村工作的新要求,构建了包括村庄、区域和流域3个层次及涵盖空气、地表水、饮用水、土壤、生态、污染点源和面源等监测内容的"十四五"农村环境质量监测体系,并提出了相应的保障措施,以期为我国农村生态环境保护提供更有力的技术支撑。     

城市化对湖泊和港湾环境的影响

全球经济的发展必然经历工业化和城市化。在城市化过程中 ,不可避免地产生工业和生活垃圾。这些垃圾不仅污染土地 ,也污染河流和湖泊 ,特别在湖泊和港湾中 ,由于水流速度变缓 ,污染物容易随着沉积物沉淀下来。又由于气候变化和人类活动 ,湖泊和港湾的沉积物会再次释放污染物而污染水体。这些污染物主要是过量的氮、磷、有毒有机物和重金属 ,由于经济和人文环境的不同 ,在不同地区污染程度有差异 ,目前在发展中国家较为严重。针对这些污染 ,人们用机械的、化学的和生物的方法来治理湖泊和港湾的污染 ,但根本上要从源头控制污染———减少污染物的排放     

characteristics of PM2.5 in rural areas of southern Jiangsu Province, China

Introduction Anumberofstudiesabroadhavedemonstratedthat atmosphericfineparticulatematter(PM2.5,dp<2.5μm)is notonlyassociatedwithatmosphericvisibilityreductionbut alsohasaclearcorrelationwiththenumberofdailydeathsandhospitalizationsasaconsequenceofpulmonarydisease(Chan,1997;Christoforous,2000;Schwartz,1996;Wilson,1997).On18July,1997,theU.S.EnvironmentalProtectionAgency(USEPA)promulgatednewandsevere standardsforfineparticulates(PM2.5)withthesizebelow2.5μm(15μg m3asannualaverage,65μg m…     

大同农村水环境污染原因分析及防治对策

文章在概述大同农村水环境状况的基础上,分析了其污染成因,并提出了保护与治理农村水环境的对策与建议.     

Can Forest-protection carbon projects improve rural livelihoods? Analysis of the Noel Kempff Mercado climate action project,Bolivia

We studied the Noel KempffMercado Climate Action Project (NKMCAP),Bolivia, to assess whether forestprotection carbon (C) projects cansignificantly benefit local people. Wehypothesized that forest protection canonly securely deliver C if significantstakeholders are meaningfully andtransparently involved, traditional orcustomary rights are recognized and theirloss compensated for, and there are directlinkages between conservation anddevelopment objective. Our researchfocused on 53 members of the communities ofFlorida, Porvenir and Piso Firme and 36secondary stakeholders. In each of thevillages we held half-day meetings withcommunity leaders, complemented bysemi-structured one-hour interviews with 5,10, and 7 families, representing 20%, 10%and 8% of each community. The long-termimpact of the NKMCAP on the localcommunities may well be positive. However,in the short run, certain sections of thelocal communities are financially poorer. Forest protection projects clearly have thepotential to sequester C, protectbiodiversity and simultaneously contributeto sustainable rural development, but ifthey really are to improve rurallivelihoods, they must be designed andimplemented carefully and participatively.