我国循环经济行业2013年发展综述

综述了2013年循环经济行业发展的政策环境及再生资源回收利用概况;重点分析了“城市矿产”建设发展,以及煤炭行业、石化行业、拆船行业的循环经济发展现状;针对行业发展中存在的主要问题提出了相关对策建议;对行业的发展进行了展望。     

我国电除尘行业2013年发展综述

综述了2013年我国电除尘行业的发展环境和经营状况;分析了电除尘行业的新技术研发进展及应用情况;简述了行业骨干企业的发展概况;针对行业发展中存在的主要问题提出了解决对策及建议,并对行业的发展进行了展望.     

我国机动车污染防治行业2011年发展综述

综述了2011年我国机动车污染防治行业的发展环境,以及行业的技术发展进展、新技术开发应用情况和市场特点;介绍了行业主要(骨干)企业的发展情况;分析了2011年行业发展中存在的主要问题,提出了解决对策和建议,并对行业的发展进行了展望。     

我国水污染治理行业2012年发展综述

综述了2012年我国水污染治理行业发展状况及发展环境;阐述并评价了行业市场运营、行业骨干企业经营、行业技术创新发展的状况;分析了行业目前的市场热点及发展趋势。     

我国噪声与振动控制行业2012年发展综述

综述了2012年我国噪声与振动控制行业的发展环境以及行业的生产经营情况;阐述了行业总体技术进展、新技术的开发应用概况,以及行业市场特点及重要动态;分析了行业主要骨干企业的发展情况及企业的国内国际竞争力状况;针对行业发展中存在的主要问题,提出了解决对策和建议,并对行业的发展进行了展望。     

我国脱硫脱硝行业2013年发展综述

综述了2013年我国脱硫脱硝行业的发展环境及发展概况;重点介绍了火电行业、钢铁行业、水泥行业脱硫脱硝产业发展现状;分析了行业市场特点及重要动态;针对行业发展中存在的主要问题提出了解决对策和建议.     

我国环境监测仪器行业2013年发展综述

综述了2013年我国环境监测仪器行业的发展环境,介绍了行业总体经营及行业技术的发展状况,阐述了2013年行业市场的特点及重要动态,提出了行业发展中存在的主要问题及对策建议。     

我国电除尘行业2010年发展综述

综述了2010年我国电除尘行业的发展环境和行业经营状况;介绍了电除尘行业总体技术进展以及新技术的开发应用情况;分析了2010年行业市场的特点及动态;针对行业发展中存在的问题提出了建议,并对行业的发展进行了展望。     

我国噪声与振动控制行业2013年发展综述

综述了2012年我国噪声与振动控制行业的发展环境以及行业的生产经营情况;阐述了行业总体技术进展、新技术的开发应用概况,以及行业市场特点及重要动态;分析了行业主要骨干企业的发展情况及企业的国内外竞争力状况;针对行业发展中存在的主要问题, 提出了解决对策和建议,并对行业的发展进行了展望.     

我国噪声振动控制行业2010年发展综述

综述了2010年我国噪声振动控制行业的发展环境以及新技术的发展和应用情况,分析了行业的市场特点及主要骨干企业的发展情况,指出了行业发展中存在的主要问题,提出了解决对策和建议,并对行业的发展进行了展望。     

Projected Changes in Discharge in an Agricultural Watershed in Iowa

Our improved capability to adapt to the future changes in discharge is linked to our capability to predict the magnitude or at least the direction of these changes. For the agricultural United States Midwest, too much or too little water has severe socioeconomic impacts. Here, we focus on the Raccoon River at Van Meter, Iowa, and use a statistical approach to examine projected changes in discharge. We build on statistical models using rainfall and harvested corn and soybean acreage to explain the observed discharge variability. We then use projections of these two predictors to examine the projected discharge response. Results are based on seven global climate models part of the Coupled Model Intercomparison Project Phase 5 and two representative concentration pathways (RCPs 4.5 and 8.5). There is not a strong signal of change in the discharge projections under the RCP 4.5. However, the results for the RCP 8.5 point to a stronger changing signal related to larger projected increases in rainfall, resulting in increased trends, in particular, in the upper part of the discharge distribution (i.e., 60th percentile and above). Examination of two hypothetical agricultural scenarios indicates that these increasing trends could be alleviated by decreasing the extent of the agricultural production. We also discuss how the methodology presented in this study represents a viable approach to move forward with the concept of return period for engineering design and management in a nonstationary world.     

Investment in human capital in Africa

Summary The author analyses the problems currently faced by the African continent, recognises six factors which he believes are important in influencing the analysis, and argues that the only secure, renewable asset any country or continent has, is its people. He maintains that people development, rather than the classical economic forms of encouraging development, offers Africa a viable way forward. He then identifies a number of specific issues within such a strategy of investment in human capital.Brian Walker is the President of the International Institute for Environment and Development (IIED), and this address was given at the inaugural meeting of the International Year of Shelter for the Homeless, in London, on 18th April, 1985. A second, earlier, associated address was published inThe Environmentalist 5(3) 167–170.     

Pesticides in rain in four agricultural watersheds in the United States

Rainfall samples were collected during the 2003 and 2004 growing seasons at four agricultural locales across the USA in Maryland, Indiana, Nebraska, and California. The samples were analyzed for 21 insecticides, 18 herbicides, three fungicides, and 40 pesticide degradates. Data from all sites combined show that 7 of the 10 most frequently detected pesticides were herbicides, with atrazine (70%) and metolachlor (83%) detected at every site. Dacthal, acetochlor, simazine, alachlor, and pendimethalin were detected in more than 50% of the samples. Chlorpyrifos, carbaryl, and diazinon were the only insecticides among the 10 most frequently detected compounds. Of the remaining pesticide parent compounds, 18 were detected in fewer than 30% of the samples, and 13 were not detected. The most frequently detected degradates were deethylatrazine; the oxygen analogs (OAs) of the organophosphorus insecticides chlorpyrifos, diazinon, and malathion; and 1-napthol (degradate of carbaryl). Deethylatrazine was detected in nearly 70% of the samples collected in Maryland, Indiana, and Nebraska but was detected only once in California. The OAs of chlorpyrifos and diazinon were detected primarily in California. Degradates of the acetanilide herbicides were rarely detected in rain, indicating that they are not formed in the atmosphere or readily volatilized from soils. Herbicides accounted for 91 to 98% of the total pesticide mass deposited by rain except in California, where insecticides accounted for 61% in 2004. The mass of pesticides deposited by rainfall was estimated to be less than 2% of the total applied in these agricultural areas.     

Environmental assessment in countries in transition: evolution in a changing context

Over the last fifteen years, Environmental Assessment systems of transitional societies of Central and Eastern Europe and Central Asia have undergone dramatic change from appraisals integrated into centrally planned economies to formal procedures aimed to ensure interdisciplinary analysis of environmental impacts and linked to publicly accountable decision-making. In most Central European nations, EA systems have been radically reformed to approximate the procedures used in developed countries, particularly in the European Union. In contrast, EA in most of the former Soviet republics has been reformed more gradually and is still based on the so-called State Environmental Review procedure inherited from the USSR and substantially different from 'Western' EA. About one-third of the transitional countries (in the Balkans, the Caucasus and Central Asia) have, so far, failed to establish functioning EA systems. Throughout the region, there has been a gap between EA legislation and practice, especially concerning interdisciplinary analysis of environmental impacts, public participation, and utilisation of EA findings in decision-making. A key driving force in the reform of EA systems has been the change in their societal context, the so-called 'process of transition'. Three main policy agendas--environmental protection, reforms of decision-making, and conforming to international requirements--along with the institutional context of EA regulations and practice have influenced both the change of EA systems over time and the regional variations in the patterns of their evolution. This study suggests that an effective reform of an EA system should be context-sensitive, or be 'in gear' with the political and economic transition. Future EA research should consider their changing societal contexts and focused on practical effects of applying EA procedures.     

Community-company relations in gold mining in Ghana

As a result of Structural Adjustment Programme from the 1980s, many developing countries have experienced an increase in resource extraction activities by international and transnational corporations. The work reported here examines the perceived impacts of gold mining at the community level in the Wassa West District of Ghana, Africa and discusses those perceived impacts in the context of globalization processes and growing multinational corporate interest in Corporate Social Responsibility (CSR). Interview data compared community members' perceptions with those of company representatives in three communities. The results indicate that communities held companies responsible for a series of economic, social, and environmental changes. While recognizing some of the benefits brought by the mines, communities felt that the companies did not live up to their responsibility to support local development. Companies responded by denying, dismissing concerns, or shifting blame. Findings from this work show that lack of engagement and action by government agencies at all levels resulted in companies acting in a surrogate governmental capacity. In such situations, managing expectations is key to community-company relations.     

电催化氧化处理难降解废水技术研究进展

电催化氧化处理难降解废水技术已得到了广泛关注.本文从电极材料与应用,电极结构及反应器形状,以及与其它处理方法联用等综述了最新研究进展,并在此基础上总结出了电催化氧化技术今后的发展方向.     

Private participation in isolated grids in Mozambique

This article presents a case study from Mozambique of the electrification of two selected towns under a World Bank financed project. Low-cost electricity services were extended to the two isolated areas after an enabling framework had been created for private sector participation. The World Bank project also demonstrates that the private sector can be attracted to participate in rural electrification schemes even in a poor country. The example shown in this article is one of the few of its kind in SubSaharan Africa.     

我国城市生态评价研究进展

城市建设带来了越来越多的生态环境问题，生态城市建设是解决这些问题的良好途径。生态城市的建设要有一定的评价体系作为支撑，本文综述了国内基于AHP方法建立的应用较为广泛的城市生态评价体系和方法，并对国内城市生态评价的现状做了分析。     

Water management problems in economies in transition

Ambitious programmes of reform in Central and Eastern Europe (CEE) are threatened by a serious deterioration of the environment. Large-scale damage of the natural environment in many forms, including water pollution has created development barriers which adversely affect the living conditions of current and future generations. Despite similar patterns of environmental policy in the CEE countries compared with their Western counterparts, neither environmental legislation nor economic incentives have produced any significant improvement in water quality over the last 10–20 years. For that very reason in the transition period, it is necessary to identify existing deficiencies in the system and to build up a mixed system of new institutions of water management, more realistic legislation with a strong enforcement system, and market based incentives for water conservation and protection against pollution.