黄河下游引黄灌区水价与水资源调控*

40多年来,我国水利建设取得了巨大成就,但是,在以往的计划经济条件下,水利事业普遍存在着“重建轻管”的问题,延续至今,尚未妥善解决,从而导致一些地区水资源的极度浪费及出现不良的环境后效。水资源管理是水资源合理开发利用的基本保证,它涉及到政策、法律、体制、经济及现代科学技术,是一个跨部门、跨学科的系统工程。目前,我国在水资源管理中最突出的问题是尚未完全纳入市场经济的轨道,水价远低于供水成本,不能发挥水费征收的经济杠杆作用,遏制水资源的浪费及合理地调控地表水与地下水资源,同时,偏低的水价也使供水部门缺乏足够的资金进行工程运营与维修,造成工程老化,降低供水效率^[1].黄河下游灌区,位于豫鲁两省境内,灌溉面积约2800万亩(186.6×10⁴hm²),多年平均引水量在100×10⁸m³左右,该灌区自50年代末引黄灌溉以来,上述问题表现尤为突出。随着黄河上、中游地区的发展,用水量增加,使黄河下游灌区的用水矛盾越来越突出。此文试图以此为典型,分析供水成本的构成、现行水价确定中存在的问题及其对水资源调控的影响,供水价问题的深入研究及水价政策的制定参考。     

发展城市地质科技 构筑地质人才高地

上要建设成现代化国际大都市,城市地质工作必须确保上海城市建设各项规划任务的顺利实现。通过总结经验,转变观念,及时把握机遇,发展城市地质科技,构筑地质人才高地,为新世纪上海城市建设大发展作出新的贡献。     

First international payment for marine ecosystem services: The case of the Banc d’Arguin National Park,Mauritania

This article investigates whether the European Union-Mauritania fisheries agreement, which allocates part of the Europe's financial contribution to the conservation of marine ecosystems located within the Banc d’Arguin National Park, can be regarded as a payment for ecosystem service. A framework for qualification as such payment scheme was established based on an extensive literature review. The criteria identified for the qualification as a payment to ecosystem service pertain to: (1) the definition of the ecosystem service(s) involved; (2) the mechanism involved by the payment; and (3) the nature of the transaction. Interviews with local beneficiaries and subsequent data analysis led to the conclusion that this mechanism could be regarded as a payment to ecosystem service and so, through the European Union-Mauritania Fisheries agreement, the European Union were investing to protect local fish resources that could be exploited by its fishing fleet. This agreement, involving the first International Payment to Ecosystem Service of this kind, marks an important step towards better consideration of marine conservation in international public policy and foreign fishing policy in particular. However, this payment is small when compared to revenues generated through the exploitation of developing countries’ fishing grounds by fishing countries. Nevertheless it opens the door for more detailed applications of payment to ecosystem service schemes to other ecosystems contexts, and can provide a useful alternative source of financing of marine biodiversity conservation.     

Property rights in fishing: from state property towards private property?: A case study of three EU countries

Fishing limitations to protect fish stocks can develop to different types of property rights. A move towards full private rights is promoted by some authors. The article questions whether such a move is desirable and it also investigates whether private rights are indeed becoming more important in EU fisheries. A study on property rights in the Danish, Dutch and UK fishery (WP Davidse, ed., Property Rights in Fishing, LEI-DLO, The Hague, 1997, OV159) sector forms the background of this approach.Bromley’s definition of property rights (D W Bromley, Environment and Economy: Property Rights & Public Policy, Blackwell, Oxford, 1991), including ‘a right to a benefit stream’, has been used to identify rights in these three EU fishing sectors. These property rights regimes vary from a domination of state property, the Danish one, to a complete system of individual rights, the Dutch case. The UK position is between these extremes, showing characteristics of common property, apart from kinds of state- and individual property of fishing rights.The article ends with a consideration of the review of the Common Fisheries Policy (CFP) in 2002 from the viewpoint of property rights. Negotiations in the run up to 2002 will demonstrate conflicts between views on state property and on private property rights. This regards the tension between the principle of relative stability of quota allocations and the EU principle of free movement of capital, goods and services. Finally, two possibilities are suggested to combine both these principles.     

US EMPLOYMENT IN FOREIGN-OWNED HIGH TECHNOLOGY FIRMS*

The spatial distribution of foreign-owned high technology firms in the United States is poorly understood, as is the degree to which emplyment in foreign-owned firms and US-owned firms coincides or differs in their distribution. Data from 1988 indicate that while total employment in foreign-owned high technology firms was not statistically different from that of US-owned firms, marked differences were evident in particular sectors, including software, advanced materials, and pharmaceuticals. By nation of ownership, only Swiss firms departed significantly from the US distribution.     

Selecting and assessing social objectives for Australian fisheries management

This paper details Australian research that developed tools to assist fisheries managers and government agencies in engaging with the social dimension of industry and community welfare in fisheries management. These tools are in the form of objectives and indicators. These highlight the social dimensions and the effects of management plans and policy implementation on fishing industries and associated communities, while also taking into account the primacy of ecological imperatives. The deployment of these objectives and indicators initially provides a benchmark and, over the life of a management plan, can subsequently be used to identify trends in effects on a variety of social and economic elements that may be objectives in the management of a fishery. It is acknowledged that the degree to which factors can be monitored will be dependent upon resources of management agencies, however these frameworks provide a method for effectively monitoring and measuring change in the social dimension of fisheries management.Essentially, the work discussed in this paper provides fisheries management with the means to both track and begin to understand the effects of government policy and management plans on the social dimension of the fishing industry and its associated communities. Such tools allow the consideration of these elements, within an evidence base, into policy arrangements, and consequently provide an invaluable contribution to the ability to address resilience and sustainability of fishing industries and associated communities.     

History,effort distribution and landings in an artisanal bottom longline fishery: An empirical study from the North Atlantic Ocean

Commercial fishing data were used to reconstruct historical spatio-temporal patterns of fishing effort and landings in the bottom longline fishery of the Azores. Key events during an important 15-year period were charted, through fisher interviews together with GIS analysis. While effort distribution varied over time, the prevailing pattern was a shift in focus from eastern to western areas and from shelf/slope to offshore banks and seamounts in response to policy measures (e.g. banning bottom longline inside 3 NM, public aids for modernization of the fleet) and reduced fishing yields. Areas 12–50 NM from shore represented the most vital fishing grounds in terms of fishing effort and production. Declining landings of the major demersal species, in recent years, indicate that present catch levels are not sustainable and further measures need to be taken in order to sustain fisheries resources. Knowledge of fleet behavior and the distribution of fishing effort, particularly in patchy environments, provide valuable insights into the impacts of past management decisions and help predict the outcome of new policies both in this region and elsewhere.     

Results based management in fisheries: Delegating responsibility to resource users

While the notion of results based management has been devoted recent attention in the context of reforming European fisheries management, it remains unclear what it entails. A conceptual model of results based management in fisheries is proposed as a way for public authorities to delegate specific management and documentation responsibilities to resource users. The model comprises three defining features: (1) That authorities define measurable objectives for the utilization of fisheries resources; (2) that resource users are made responsible for achieving these objectives and for (3) providing documentation that allows for an audit of the extent to which they are met. Selected cases are used to illustrate these features. Rationales and prospects of introducing results based management as an alternative in a European fisheries management context are discussed, giving consideration to how it may be pursued under the reformed common fisheries policy.     

Ballast water management in Canada: A historical perspective and implications for the future

Non-indigenous species (NIS) can create significant risks when introduced to foreign ecosystems. One of the many vectors facilitating the global transport of NIS is ballast water, and as commercial shipping increases so does the threat of ballast water-mediated introductions. Despite Canadian regulations, consistent with international guidelines put forth by the International Maritime Organization in the early 1990s, ballast water remains a potential vector for the introduction of many NIS to Canadian marine ecosystems: there have been no new introductions in the Laurentian Great Lakes Region since 2006, yet marine ecosystems continue to see the introduction and establishment of NIS. This paper details and analyzes the development of Canadian ballast water management (BWM), in the context of marine ecosystems, and identifies issues therein. BWM in Canada has a number of management gaps that have persisted since large-scale BWM began in the late 1980s. These include BWM exemptions for vessels not exiting the North American continental shelf, and limitations of effectiveness of mid-ocean exchange as the predominant management method in marine ecosystems. In addition, ballast water regulations for the Canadian Arctic may require additional consideration as the Arctic will likely continue to see an increase in both warming and commercial shipping in the future, thereby increasing the potential risk of NIS. In order to adequately protect all Canadian marine ecosystems, it is recommended that the current BWM regime: fill gaps in management to help prevent further introduction and spread of NIS; focus equally on both marine and freshwater regions, and; look to other aggressive BWM strategies such as those being developed by the state of California.