REASONABLY FULL HYDROLOGIC DEVELOPMENT OF RESERVOIR SITES1

The size of multipurpose reservoir development is usually determined by an economic analysis of reservoir capabilities and the present and projected water resources needs which can be satisfied. This analysis is referred to as project formulation, wherein optimum conditions are sought. In responding to multiple objectives, i.e., national economic development, regional development and environmental quality, which are being considered in river basin planning in recent years, reservoirs should provide for reasonably full hydrologic development. Additional storage will be needed to provide opportunities for economic development, as well as meet unexpected development. Also, it provides more flow regulation capability for quality of environment considerations. An analysis has been made on twelve reservoir sites in the New York State portion of the Susquehanna River Basin to determine the so-called “reasonably full hydrologic development of reservoir sites.” Hydrologic, economic, environmental and physical characteristics of the sites are taken into consideration. For normal conditions, it can be concluded that a yield equivalent to about 80 percent of the average discharge (runoff) can be considered as reasonably full hydrologic development for reservoir sites in the Susquehanna River Basin in New York. The same technique can be applied elsewhere to determine reasonably full hydrologic development of reservoir sites.     

SOCIO-ECONOMIC CONSIDERATIONS IN WATER RESOURCES PLANNING1

Historically, the main objective of water resources development has been economic efficiency, and the technique for its evaluation has been benefit-cost analysis. Gradually other objectives have emerged, and these in order of their emergence are regional income redistribution, environmental quality and social well-being. These multi-objectives have given rise to multifarious problems, and have made the planning process much more complex than ever before. The different objectives are not mutually exclusive, and, hence, contributions to one can only be made at the expense of others. Trade-off studies between different objectives are difficult to make. It is suggested that one way to overcome this difficulty could be to design a system to perform optimally in terms of one objective, subject to a specified level of performance of the other, which in effect becomes a constraint. The paper also discusses the pros and cons of the desirability of public participation in our decision-making processes, and the necessity of developing social sciences models to aid water planning and management.     

生态环境损害赔偿诉讼：定义与定位矫正

面对生态环境损害赔偿诉讼这一新型诉讼形式,准确把握其定义和定位至关重要。现有生态环境损害赔偿诉讼按国家自然资源所有权私权化路径进行制度构建,其现行定义为特殊私益诉讼,现行定位为环境行政替代工具。这种定义与定位导致其与环境公益诉讼割裂,运行序位上优先于环境民事公益诉讼,引起国家机关角色错位。生态环境损害赔偿诉讼与环境民事公益诉讼的诉讼标的相同,救济和保护的利益均为环境公益,其定义应回归公益诉讼本位;政府在环境公益保护上有着广泛的职权和手段,是环境公共治理的优先主体,仅在少数行政不能的情形下才有借助司法的必要性和合理性,其在定位上应作为环境行政执法的补充机制在有限范围内发挥作用。据此,生态环境损害赔偿诉讼在制度体系上应与既有环境民事公益诉讼置于同一诉讼系属统筹立法,在诉讼序位上应让位于社会组织提起的环境民事公益诉讼。     

清洁生产纳入环境影响评价的意义

当前的环境影响评价在某种程度上更侧重于环境的末端治理,无法将污染控制与生产过程控制密切结合,资源和能源不能在生产过程中得到充分利用.而清洁生产在这方面却有着独特的特点和优势.根据清洁生产与环境影响评价的内在联系,尽快地将清洁生产纳入环境影响评价是具有重要意义的,清洁生产应该成为环境影响评价报告撰写中的重要内容.     

持续发展是唯一出路

不适当的发展模式已使人类、环境与发展之间形成恶性循环，必须及时地改变发展模式。列举了中国面临的严重环境问题，指出只有持续发展才是中国的唯一出路。提出应注意的问题有：推行清洁生产，发展生态农业，保护资源，促进城市可持续发展，环境污染防治，修复受污染的环境等。     

促进我国环保产业发展的税收政策研究

阐述了税收政策介入环保产业发展的理论基础，即外部性和公共产品理论决定了环保产业的发展需要税收优惠政策给予支持；分析了我国现有环保产业的所得税政策、增值税政策和营业税政策；提出了应完善现有税制及税收分配体制等促进我国环保产业发展的税收政策建议。     

Evolution of environmental impact assessment as applied to watershed modification projects in Canada

This article reviews the application of environmental impact assessment (EIA) procedures and practices to three watershed modification projects situaled in western Canada. These ventures were justified for accelerating regional economic development, and cover the period during which public concerns for protecting the environment rapidly made their way into the national political agenda. An historical account and analysis of the situation, therefore, seems desirable in order to understand the development of EIA processes, practices, and methodologies since the start of construction of the first project in 1961. This study concludes that there has been good progress in predicting and evaluating environmental and related social impacts of watershed modification proposals. However, a number of obstacles need to be overcome before EIA can firmly establish itself as an effective planning tool. These difficulties include jurisdictional confusions and conflicts, division of authority and responsibility in designing and implementing appropriate mitigative and monitoring measures, lack of tested EIA methodologies, and limited availability of qualified human resources. A number of conclusions and suggestions are offered so that future watershed modification proposals may be planned and implemented in a more environmentally sustainable fashion. These include: (1) EIA processes must be completed before irrevocable decisions are made. (2) Any major intrusion into a watershed is likely to impact on some major components of the ecosystem(s). (3) Mitigation costs must form part of the benefit-cost analysis of any project proposal. (4) Interjurisdictional cooperation is imperative where watersheds cross political boundaries. (5) The EIA process is a public process, hence public concerns must be dealt with fairly. (6) The role of science in the EIA process must be at arms length from project proponents and regulators, and allowed to function in the interest of the protection of the environment and public health and safety. The views expressed here are the authors’ own and do not necessarily reflect those of FEARO and/or other government agencies and officials involved in the review of these projects.     

Managing environmental impacts of energy development: Air quality in the Hunter Region,New South Wales,Australia

The Hunter Region in New South Wales, Australia, is undergoing rapid economic development based on its black coal resources. Cumulative impacts of new projects cannot be easily assessed with the traditional environmental impact statement. This article examines air quality impacts, and presents a systems analysis model to assist environmental management. The model consists of an input-output model of the regional economy and an air dispersion model. Results are obtained for sulfur oxides and fluorides.     

论生活社区污染物的就地分散处理

我国目前的生活社区污染物治理方式主要是收集后集中处理,这种处理方式存在若干问题,如会影响集中处理场所和转运沿线周边社区的环境质量、不利于处理产物的资源化利用、收集系统的成本较高等。文章提出生活社区污染物宜就地处理,使本社区的污染物不会转移到其他社区,同时便于污染治理产物的资源化利用,而且可以促进环保产业升级,提高农村社区居住环境质量,促进绿色农业的开展,减轻政府环保工作压力。     

Energy policies and environmental security: A multi-criteria analysis of energy policies of Pakistan

Access to affordable and efficient energy is a basic human right and an imperative for human development. The energy policies usually ponder technical, economic, environmental, and social aspects for successful procurement of energy and endowment of energy resources. The objectives of this paper are to analyze energy policies in Pakistan and assess their relationship with environmental security and development. An empirical and multi-criteria decision analysis was used to unfold the strong interactions of energy security with development and environment. The energy policies in Pakistan are more equipped with economic and technical aspects, fairly framed with social aspects and poorly pampered with environmental facets. The dearth of environmental aspects will not only results in environmental degradation but also lag the development and achievement of Sustainable Development Goals.     

THE NEED FOR A COMPREHENSIVE APPROACH IN THE MANAGEMENT OF ENVIRONMENTAL RESOURCES1

ABSTRACT Environmental resources can be managed properly only by adopting a comprehensive approach. The whole environment must be considered as a single system, and prior to any action, all types of environmental impacts caused by it should be studied in detail. This paper underlines the close relationship between different environmental problems, analyzes existing management patterns, and proposes new alternatives whenever applicable. The different constraints, which have to be considered in the decision-making process while developing a plan, are also discussed. It is concluded that efforts neglecting the interaction among different aspects of the environment do not upgrade the quality of water, air, and land to any appreciable degree.     

A Role of Fair Trade Certification for Environmental Sustainability

Although most studies on the Fair Trade initiative are, to some extent, cognizant of its contribution to environmental sustainability, what the environmental aspect means to Fair Trade has not yet been explored fully. A review of environmental issues in the Fair Trade literature suggests that Fair Trade might influence participant producers’ farming practices even if it does not directly impact natural resources. This paper attempts to interpret Fair Trade certification as an intermediary institution that links two significant objectives of rural development in the global South—environmental conservation and poverty reduction. This theoretical concept is examined in different real settings by observing four cases of Southern small farmer groups involved in the Fair Trade initiative. Findings from these case studies imply that if Fair Trade certification ensures tangible benefits for small farmers, it can not only help such disadvantaged farmers but also work as an approach for natural resource management.     

将环境规划纳入国民经济和社会发展规划中的方法初探

社会经济发展的最终目的是提高人民的生活质量,而环境质量是生活质量的重要组成部分,因此环境质量的优劣无疑应成为评价生活质量是否提高的标准之一.同时,保证资源具有可持续的支撑能力更是实现社会经济可持续发展的关键.因此,社会、经济发展规划中应体现出环境与资源因素的影响,这就需要开发现实可行的方法,以用于制定有利于实现可持续发展的区域规划.本文从物质平衡的角度出发,利用投入产出分析作为中介体,针对区域发展的特点提出了将环境成本和资源价值体现在区域投入产出分析中的方法,并探讨了如何将这种方法应用于区域规划研究中.     

Setting rational environmental goals: Five Swedish environmental quality objectives

Goals and performance targets are commonly used as tools in the policy-implementation process. In Sweden, environmental policy is operationalized through a system of environmental quality objectives that were adopted by the Swedish Riksdag in the late 1990s. The objectives describe what level of environmental quality Sweden should aim for within a generation, and are designed to guide decision making in all sectors of society. However, to guide decision making toward improved environmental quality, these objectives should satisfy a set of rationality (functionality) criteria; they should be precise, evaluable, approachable, motivating and coherent. In this paper, five Swedish environmental quality objectives are investigated through an application of the suggested criteria: (1) a balanced marine environment, flourishing coastal areas and archipelagos; (2) a magnificent mountain landscape; (3) a non-toxic environment; (4) natural acidification only; and (5) a good built environment. The aim of the paper is to bring the rationality of the objectives up for discussion, and to illustrate the range of issues and difficulties that are involved in choosing and assessing environmental policy goals.     

Think globally,act locally: neighbourhood pollution and the future of the earth

Each year governments and industry around the globe spend billions of dollars in search of treatments and cures for diseases that shorten lives, which often means gadgets, implants, radiation and pills. These “cures”, do not get to the root of the problem. Perhaps it is time for us to adjust our thinking to be more proactive instead of reactive in public health. Perhaps we need to consider confronting environmental pollution of air, soil and water at a local level. As the Physicians for Social Responsibility point out, we should be “preventing what we cannot cure”. One such preventive measure is ensuring that our communities, including our poor inner-city neighbourhoods, enjoy a clean environment. We challenge local and national policy-makers to respond to the global call and to take action to address environmental toxins; to take local action to ameliorate the pollution of the air, water and soil in so many of our nation’s neighbourhoods. A person’s neighbourhood, and the proximity of dangerous environmental contaminants within it, is a powerful predictor of how long s/he will live. While situations like the poisoning of the water in Flint, Michigan have gotten some attention, they are generally treated as the exception rather than a reflection of real environmental hazards that exist in the west. Moreover we wonder why more endemic issues of neighbourhood environmental contamination that shorten human lives are not a priority for local action or that it is not linked to disproportionate production of greenhouse gases that cause climate change/warming/chaos.     

THE CONTINUING EVOLUTION OF AN AUSTRALIAN WATER RESOURCES POLICY1

ABSTRACT: Australia's extremely limited water resources highlight the need for policy guidelines for management. During the 1970s, there was the gradual evolution of a national water resources policy, facilitated by a nationally agreed statement of objectives and culminating in a federal policy statement presented in 1979. However, the Australian constitution gives major responsibility for water resources to the states. Further, the federal policy statement seems to assume that each state has a water resources policy and that it accords with the nationally agreed objectives. This is not the case, and the practical management of Australia's water resources falls short of the principles set out in the policy document. The River Murray, the nation's major water resource, provides ample evidence of this fact. With very limited water resources, Australia urgently needs to reduce the disparity between principle and practice in their management.     

浅论危险废物和医疗废物处置项目环评工作中应注意的问题--以阿克苏地区危险废物处理项目为例

危险废物和医疗废物安全处置一直是人们关注的一个问题,以新疆阿克苏地区危险废物和医疗废物处置项目的环评为例,分析讨论了环评工作中应注意的问题,以有效减小废物处置过程中的环境风险,为实现危险废物和医疗废物的无害化集中处置做了有益的探索.     

An evaluation paradigm for cumulative impact analysis

Cumulative impact analysis is examined from a conceptual decision-making perspective, focusing on its implicit and explicit purposes as suggested within the policy and procedures for environmental impact analysis of the National Environmental Policy Act of 1969 (NEPA) and its implementing regulations. In this article it is also linked to different evaluation and decision-making conventions, contrasting a regulatory context with a comprehensive planning framework. The specific problems that make the application of cumulative impact analysis a virtually intractable evaluation requirement are discussed in connection with the federal regulation of wetlands uses. The relatively familiar US Army Corps of Engineers' (the Corps) permit program, in conjunction with the Environmental Protection Agency's (EPA) responsibilities in managing its share of the Section 404 regulatory program requirements, is used throughout as the realistic context for highlighting certain pragmatic evaluation aspects of cumulative impact assessment.To understand the purposes of cumulative impact analysis (CIA), a key distinction must be made between the implied comprehensive and multiobjective evaluation purposes of CIA, promoted through the principles and policies contained in NEPA, and the more commonly conducted and limited assessment of cumulative effects (ACE), which focuses largely on the ecological effects of human actions. Based on current evaluation practices within the Corps' and EPA's permit programs, it is shown that the commonly used screening approach to regulating wetlands uses is not compatible with the purposes of CIA, nor is the environmental impact statement (EIS) an appropriate vehicle for evaluating the variety of objectives and trade-offs needed as part of CIA. A heuristic model that incorporates the basic elements of CIA is developed, including the idea of trade-offs among social, economic, and environmental protection goals carried out within the context of environmental carrying capacity.     

Systems vs. metasystems: EMIS at the crossroads

As environmental management responsibilities expand beyond regulations to address business issues such as design for the environment, total cost accounting, and strategic planning, it is tempting to plan for expanded information systems (EMIS) to handle new responsibilities. The author argues that we should pursue exactly the opposite course: shrink the EMIS to the minimum size possible. It would be impossible to feed the self-standing EMIS with all the data it needs—replicas of almost any data tracked by the organization. The EMS and EMIS should be “meta-systems” that store the organization's knowledge about how EH&S relates to various business processes, and what should be measured and reported to assure that EH&S objectives are met. The author provides examples of how companies are creating these EMS “metasystems” by leveraging enterprise systems implemented for accounting, business planning, groupware, maintenance, and process control.     

NEPA AND A STATE'S ROLE IN WATER RESOURCES MANAGEMENT1

ABSTRACT The National Environmental Policy Act of 1969, has been called a revolutionary piece of legislation. It has changed, and is still changing the traditional ways of governmental decision-making. NEPA has strongly influenced the field of water resources management. An environmental statement can now be seen not as a document to support or justify a plan, but an objective assessment of what environmental costs and benefits are involved. New York State has seized upon NEPA as an important feature of its environmental quality management programs and has used the opportunity to comment upon draft environmental statements under NEPA to increase its influences upon Federal decision-making. The Department of Environmental Conservation coordinates and synthesizes all comments and provides one unified State response on a statement. At the State level, lacking a comprehensive “little NEPA”, an extensive environmental analysis program has been built by utilizing a wide spectrum of Federal and State Laws and administrative regulations.