白石砬子自然保护区几种主要植被类型土壤入渗特性研究

为了深入研究辽东山区森林土壤的水源涵养功能,以白石砬子自然保护区内的6种主要植被类型下土壤为研究对象,采用野外双环试验和室内理化性质分析相结合的方法,研究了不同植被类型下土壤入渗能力及其与理化性质的关系。结果表明,不同植被类型土壤的初渗率、稳渗率、平均入渗率、渗透总量均表现为下层低于上层,最大值是最小值的近3倍;不同植被类型间土壤入渗能力差异较大,其中A层初渗率排列顺序为原生红松阔叶混交林>红松人工林>鱼鳞云杉臭冷杉林>农地>蒙古栎林>杂木林,B层初渗率排列顺序为鱼鳞云杉臭冷杉林>农地>杂木林>红松人工林>原生红松阔叶混交林>蒙古栎林,A层稳渗率排列顺序为红松人工林>鱼鳞云杉臭冷杉林>原生红松阔叶混交林>杂木林>蒙古栎林>农地,B层稳渗率以杂木林最大,为3.8 mm?min-1,原生红松阔叶混交林最小,仅为1.1 mm?min-1,其他4种植被类型土壤稳渗率几乎无差异,A层平均入渗率排列顺序为红松人工林>原生红松阔叶混交林>鱼鳞云杉臭冷杉林>杂木林>蒙古栎林>农地,B层平均入渗率排列顺序为杂木林>鱼鳞云杉臭冷杉林>红松人工林>蒙古栎林>农地>原生红松阔叶混交林,A层的渗透总量以红松阔叶混交林和红松人工林最大,蒙古栎林和农地相对较低,B层的渗透总量以杂木林最大,红松阔叶混交林最小;主成分分析评价的土壤入渗能力排序为红松人工林>鱼鳞云杉臭冷杉林>原生红松阔叶混交林>杂木林>蒙古栎林>农地,初渗率、稳渗率、平均入渗率和渗透总量等4个指标综合起来能够很好的表达土壤入渗能力,其主成分方差的累积贡献率为90.662%;不同层次土壤入渗速率与入渗时间均存在良好的幂函数关系;土壤的稳渗率、平均入渗率、渗透总量与非毛管孔隙度呈显著正相关关系,初渗率与非毛管孔隙存在相关性,但不显著。与容重存在负相关关系,但不显著。     

生态系统服务价值评估的研究进展

生态系统服务价值评估是当前生态经济学和环境经济学的研究焦点。首先回顾了国内外关于生态系统服务功能的概念和分类的研究;其次根据发展历程分析了国外生态系统服务价值的评估研究;然后从全国、区域以及单个生态系统等方面探讨国内生态系统服务价值评估的研究。最后指出现有生态系统服务价值评估研究中的不足及今后发展方向,以期丰富生态系统服务价值评估理论。     

宏基因组学分析深度处理阶段污水中细菌的赋存特征及其功能

为探究深度处理阶段污水中细菌的赋存特征及其功能,采集了污水深度处理阶段沿程各单元的进出水样品,并基于宏基因组学对污水中细菌的群落结构及功能进行了解析.结果表明,不同深度处理单元出水中细菌的多样性存在差异,臭氧接触池出水中细菌的多样性最低;相比夏季,冬季深度处理阶段污水中细菌的丰富度和多样性较低.不同季节深度处理阶段污水中的细菌群落结构变化较大,反硝化滤池出水中的细菌群落结构与其它样品存在较大差异;变形菌门（41.5%～71.0%）是深度处理阶段污水中的主要优势菌门,其次是拟杆菌门（3.8%～16.2%）;反硝化滤池出水中主要菌属有脱氯单胞菌（4.1%～7.4%）、弓形杆菌（3.0%～8.3%）和不动杆菌（2.3%～3.0%）.在深度处理阶段各工艺出水中共发现了29种与氮代谢有关的功能基因,并且在各工艺出水中均检测到了与反硝化有关的功能基因,如nosZ、napA、nirK和norB等,表明深度处理阶段污水中的细菌具有持续脱氮的潜力.糖苷转移酶和糖苷水解酶是深度处理阶段主要的碳水化合物活性酶,深度处理阶段污水中的细菌表现出了对多种有机物的降解潜力.     

开发建设项目生态环境影响评价原则─生态环境功能保护论

地球各类生态系统是人类可持续生存与发展所依赖的环境,即生态环境,从可持续发展战略出发,在开发建设项目的环境影响评价中应注重生态环境影响评价。本文提出,生态环境影响评价应从保持生态系统的环境功能着眼,评价生态功能所受的寻求功能补偿的措施。文中列出１２项以上的生态环境功能和建议进行的价值计量方法。同时指出,进行生态环境功能影响评价必须树立三种观念;（１）区别于传统经济观念的生态资源价值观,并从土地利用     

大叶碎米荠的开发与利用

我国野菜资源十分丰富,野菜大多具有较高的营养保健作用,开发潜力大,市场前景十分广阔。大叶碎米荠在民间食用较多,但其开发利用还未引起人们的重视。主要介绍了大叶碎米荠的营养价值、药用价值及其开发利用方式。     

The effect of calcium and pH on nickel accumulation in and rhizotoxicity to pea (Pisum sativum L.) root-empirical relationships and modeling

The accumulation and rhizotoxicity of Ni to pea were investigated. Calcium, H, and Ni competed for root-binding sites with high pH and low Ca favoring more Ni accumulation. At low pH, Ca accumulation is the key factor determining root growth, while at medium to high pH, root elongation is more sensitive to Ni concentration. The tissue concentration of Ni and Ca ([Ni]t or [Ca]t, μmol g⁻¹ dry root) can be predicted from total dissolved Ni ([Ni]_T, μM), pH, and total dissolved Ca ([Ca]_T, mM) by two approaches. Approach 1 is the empirical equations [Ni]t = (0.361 pH-0.695[Ca]_T)*[Ni]_T and [Ca]t = 8.29 pH + 10.8 [Ca]_T. The second approach involves a two-step model. The surface-bound Ni and Ca are estimated from a surface adsorption model with binding constants derived from independent ion adsorption experiments. Then transfer functions are used to predict internal root Ni and Ca accumulation.     

Valuing lagoons using a meta-analytical approach: methodological and practical issues

Lagoons are naturally complex ecosystems whose dynamics are strongly influenced by anthropic factors. Therefore, their value depends not only on their characteristics but also on the nature of the interactions, whether positive or negative, between mankind and nature. Starting from a representative set of 31 original studies exclusively devoted to coastal lagoons valuation, we estimate a meta-analytic function of value transfer. Using a resampling technique, we then determine a transfer value and find a mean transfer error of 87% and a median error equal to 24%, between the predicted value and the original ones. This raises the problem of divergences between individual valuations for natural assets.     

Environmentally Sensitive Productivity Analysis of the Canadian Pulp and Paper Industry, 1959-1994: An Input Distance Function Approach

This study employs a parametric input distance function that incorporates both desirable and undesirable outputs to provide a more complete representation of the production technology from which environmentally sensitive productivity and efficiency measures can be generated. This framework also generates pollution abatement cost estimates that are useful for policy making. An input-based Malmquist index of productivity growth that appropriately credits the producer not only for increases in marketable or desirable outputs but also for the production of improved environmental quality through pollution abatement activities is derived from the input distance function. The method was applied to time series data from the Canadian pulp and paper industry. Our shadow price estimates indicate that the marginal cost to producers of pollution control has been rising. The main conclusion of this study is that productivity improvement, from the social viewpoint, has been stronger than conventional measures would suggest.     

地表水-地下水的交错带及其生态功能

地表水与地下水的相互作用在全球水循环中发挥着重要的作用,交错带是地表水-地下水相互作用的重要桥梁和纽带,并成为生态水文学这一新的研究领域的前沿课题。地表水-地下水的交错带是地表水与地下水的混合区域,该区域内生物地球化学活动强烈。地表水-地下水的交错带主要受自然因素和人为因素的影响。交错带内常发生物理作用、化学作用和生物作用过程,并影响交错带中水分的运动过程、溶质迁移过程和生物活动过程。交错带在水生生态系统中具有重要的功能,主要体现在缓冲作用、提供生物栖息地、提供食物、提供残留物种的保护区。交错带过程的模拟、观测方法和交错带内的生物地球化学过程和示踪以及交错带的生态功能值得进一步关注和深入研究。     

From data and theory to environmental models and indices formation

A prerequisite for environmental indices is that they represent environmental pressure, and the state of, and impact on environmental conditions. In other words, they should capture as much as possible of the cause-effect chains they represent and relate pressure and effect to criteria of environmental quality. The approach proposed in the article attempts to link the pressure–state–impact–response framework of indicators to the integrated environmental model, based on the method of response function (MRF). The MRF allows to construct purposeful, credible models from data and prior knowledge or information. The data are usually time series observations of system inputs and outputs, and sometimes of internal states. The output of such models is presented with highly aggregated environmental indices, reflecting the main pressure–state–impact–response cause-effect chains. The proposed approach is illustrated with the example of soil erosion indices.