航路改革后长江安徽段上行大船航迹线规划研究

针对航路改革后的长江安徽段上行大船航迹线如何重新规划问题,以实船试验为依托,测算出船在不同水深点上的速度;比较船在缓流中的速度增加率与船在浅水中的速度减小率的乘积.结果显示:船舶当处在相对水深为2.15的点上时,乘积最大,无岸壁效应,并通常能满足分隔效果,故应将此点作为安全与经济船位,此类船位的连线即为安全与经济航迹线.     

浅析内河船舶碰撞事故的若干特性

文中提出了内河船舶碰撞事故所具有的一些基本特性，列举了大量具体数据、实例，从事实上进行了详细的分析，并结合水上交通碰撞事故某些个性从管理的基本原理出发加以探析。只有关注和研究船舶碰撞事故特性，才能减少或避免碰撞事故的发生。     

南通哨口板鹞风筝综述

南通板鹞风筝历来以优美的造型,精湛的工艺和独特的音响效果而闻名于世。文章在叙述南通板鹞风筝社会功用及历史演变的基础上,对其独具特质的艺术形式和工艺手法进行了总结和归纳。最后,对南通板鹞风筝在当代的传承与发展进行概括和展望。     

舟山北部水域大型泊位规划对通航效率影响的仿真模拟研究

远期规划的舟山北部水域大型泊位高达50余个。进港航速低、历时长、乘潮和靠泊时间窗口要求特殊,是大型船舶影响港口通航效率的主要因素。在现状及近、远期港口规划条件下,基于Arena仿真建模方法,构建舟山北部水域大型船舶进出港仿真模型,定量统计分析不同阶段大型泊位规划对船舶通航效率的影响。结果表明:近、远期规划实施后大型船舶流量增加33%和65%,远期规划中黄泽作业区的船舶平均等待时间较现状增加约10.5 h,小洋山作业区和鼠浪湖作业区分别增加约0.5 h和2 h,对通航效率整体影响有限。     

黄河三角洲滩海油田岸滩防护方案探索

针对飞雁滩油田的岸滩侵蚀情况提出几种岸滩防护设想并确定防护方案.该方案充分利用自然力,通过人为干扰促使防护区外泥沙起动,借助海上潮流使高含沙海水流经防护区,实现岸滩蚀退的快速防护.     

沿海开发战略下的南通外语教育生态发展研究

文章运用教育生态学原理以江苏沿海开发战略为背景，分析了南通外语教育生态发展存在的问题，并提出了相应的对策。该研究对促进南通外语教育的可持续发展具有一定的借鉴意义。     

Impact of coastal construction on coral reefs in the U.S.‐affiliated pacific Islands

Abstract

During the past century, traditional ownership, control, and use of coral reef habitats in the U.S.‐affiliated islands in the Pacific have declined, exposing them to increased construction for plantation, transportation, military, urban, aquaculture, fisheries, mineral, and resort development. Dredging, filling, and other construction in coral reef and related ecosystems are expected to continue at high levels. Collectively, these activities have resulted in major adverse ecological impacts, many of which can be avoided or reduced to minor levels. Improvements in the design, siting, and construction of coastal projects can be accomplished by early integration of environmental objectives. Ecological baseline surveys; environmental impact assessments; regulatory conditions; guidelines and standards during construction; monitoring of construction; post‐construction evaluation; and long‐range research, planning, and management are among the most useful of the environmental tools to describe reefs and to identify measures to reduce or avoid adverse impacts on coral reefs.     

CZM in California: Successes and Challenges Ahead

California has a forty-year history of successful coastal zone management. The San Francisco Bay Conservation and Development Commission, the California Coastal Commission, and the State Coastal Conservancy have protected and made accessible hundreds of miles of shoreline. While each agency has played a critical role, this article focuses on the Coastal Commission. Implementing the California Coastal Act, the Coastal Commission has partnered with local government, other agencies, nongovernmental organizations (NGOs), and the public to concentrate new development in already developed areas, and much of the rural coastal zone looks as it did in 1972. The Commission has protected and expanded public shoreline access through its regulatory actions. Using strong ecological science the Commission has protected a wide variety of sensitive habitats and wetlands. And under the authority of the Coastal Zone Management Act, the Commission has reviewed thousands of federal projects to assure that they are consistent with the Coastal Act. Challenges continue, though, including population growth, sea-level rise, and inadequate funding to update local coastal land use plans to address new issues, such as climate change adaptation. New investment is needed at the national, state, and local level to continue the success of the California program.     

Democratization of Coastal Zone Decision Making for Indigenous Australians: Insights from Stakeholder Analysis

Community participation has become something of an orthodoxy within natural resource management. In the absence of an explicit strategy for democratization and capacity-building the notion of community participation is potentially meaningless and its application likely to mask decisions made in the interests of elite groups. This article examines the shortcomings of participatory processes in coastal resource management and seeks to identify and overcome constraints to democratization and capacity-building for Indigenous Australians. Using two coastal catchments in Central Queensland as a case study, we explore relations of power among stakeholders using Stakeholder Analysis to provide a platform for more effective deliberative participation by this group of stakeholders. Discussion of the specific barriers to participation identified by Aboriginal stakeholders will demonstrate the need to adopt notions of capacity-building that focus not only on the attributes of the individual stakeholder that might facilitate their participation, but on the characteristics also of the decision-making environment.     

Exposure of Fauna to Off-Road Vehicle (ORV) Traffic on Sandy Beaches

Driving of off-road vehicles (ORVs) on sandy beaches is common and widespread, but is not universally embraced due to putative environmental impacts on beach biota. For ORVs to impact the beach fauna, traffic areas must overlap with faunal habitat: a fundamental pre-requisite for impact assessments but as yet un-quantified for sandy beaches. Thus, this study quantified the spatial and temporal patterns of ORV traffic on five Australian beaches, and measured the degree to which the distribution of intertidal macro-invertebrates overlaps with traffic zones. Traffic volumes on beaches can be considerable (up to 500 vehicles per day). The position of beach traffic across the beach-face is principally governed by tides and driver behavior. Despite driver education campaigns to the contrary, a considerable fraction of vehicles (16–67%) traverses the soft, upper shore near the foredunes. The majority (65%) of burrowing invertebrate species of the intertidal zone is directly exposed to traffic, save for species inhabiting the swash zone. Because beach traffic presents a formidable management challenge, a fundamental first step in identifying whether ecological impacts are indeed likely, is to assess the potential for spatial and temporal conflict between human pressures (e.g., ORVs) and biological resources (e.g., beach fauna). Although this potential is certainly substantial for sandy shores used by ORVs, the actual ecological impacts on the intertidal fauna can only be predicted in situations where the responses (e.g., direct mortality, behavioral changes) of individual species to beach traffic are known.