三峡澎溪河回水区消落带岸边土壤重金属污染分布特征

在对澎溪河回水区消落带及岸边土样品中重金属含量和样品理化性质测定的基础上,重点分析了该区域内重金属分布特征,并对重金属元素间的相关性展开研究.同时,应用地累积指数对研究区域污染现状进行评价.结果表明,消落带样品中Cu、Cr、Zn、As、Cd、Pb、Hg的平均含量分别为28.17、59.21、108.98、4.77、2.02、28.85、0.52mg·kg-1;岸边土样品中重金属的含量范围分别为22.32、54.90、98.05、7.87、0.77、22.97、0.94mg·kg-1.Cd是三峡库区污染较严重的重金属元素.相关性分析表明：在消落带样品中,Cd与Zn显著相关（p〈0.01）,Pb、Hg和Cu、As都存在显著的正相关关系,说明这4种重金属元素在接受外来污染时可能存在相似性;在岸边土样品中,Cd与Zn、Cr与Cu、As与Hg显著相关（p〈0.01）,Pb与Cu、Cr、Zn、Cd显著正相关,表明这几种重金属可能有着相似的来源.消落带样品重金属污染程度评价结果为：Cd〉Hg〉Zn〉Pb〉Cu〉As〉Cr,岸边土样品重金属污染程度评价结果为：Hg〉Cd〉Zn〉As〉Pb〉Cu〉Cr,Cd和Hg在个别站位达到了严重污染水平.消落带土壤受人为扰动后会成为水体的二次污染源,因此,消落带土壤重金属对水体的潜在影响不容忽视.     

河水-地下水交互带沉积物中抗生素和代谢产物提取方法优化及其分布特征

河水-地下水交互带是污染物发生富集、降解和转化等生物地球化学过程的重要场所.抗生素作为一类广泛关注的有机污染物,探索其在交互带中的分布特征对认识特殊生境下污染物迁移转化过程具有重要意义.由于交互带氧化还原条件变化敏感,沉积物组成特殊,建立了一种有效提取交互带中22种抗生素及4种磺胺类代谢产物的前处理方法,并对样品初始状态、提取温度、提取液p H值以及有机提取溶剂进行了优化.同时对汉江下游河水-地下水交互带沉积物中的抗生素含量进行分析,结果表明,采用p H=3的乙腈/乙二胺四乙酸二钠(Na₂EDTA)-Mcllvaine缓冲液(1∶1,体积比)对未经氧化的沉积物原样在40℃条件下进行3次微波提取,目标抗生素的回收效果最好.汉江下游交互带沉积物中共检出11种抗生素,其中以土霉素(OTC)和氧氟沙星(OFL)为主,最高检出含量分别为6.77 ng·g^-1和5.81 ng·g^-1.不同交互剖面中抗生素含量的垂向分布差异较大,主要与沉积物岩性、抗生素理化性质和地表水-地下水交互作用等影响因素有关.     

多因素影响下巷道变形特性数值模拟研究

基于FLAC3D有限差分软件对开挖深度、侧压力系数、断面形状等多因素影响下的巷道变形参数进行正交试验，根据正交试验分析结果，分别选取同一深度条件下的圆形、马蹄形、直墙拱形、矩形巷道进行模拟试验并以圆形巷道作为典型断面，对不同深度下的巷道变形特征进行模拟试验。研究结果表明:开挖深度对巷道开挖后的应力差变化影响明显，断面形状对巷道围岩内的塑性区深度和具有显著影响；巷道开挖后的塑性区深度和随形状指数增加而呈线性增长趋势，圆形巷道的塑性区深度和最小，矩形最大；应力差随着巷道开挖深度的增加呈线性增加，深部开采应重视巷道内的应力分布情况。     

海岸带可持续发展的系统综合管理模式初探

本文在简要讨论了海岸带及其资源可持续开发利用的基础上，提出了海岸带管理的整合模式──系统综合管理模式。并详细分析了海岸带系统综合管理模式的内容和方法。     

江苏省沿江开发区空间分工、制造业集聚与转移

基于新经济地理学相关理论，针对江苏省沿江开发战略实施以后，制造业空间可能存在的变动，在整理和分析调查问卷资料的基础上，选择专业化指数和基尼系数2种方法来定量分析江苏省21个沿江省级以上开发区空间分工、制造业集聚和转移态势。结果表明：（1）2002~2006年江南沿江开发区通过向江北沿江开发区转移部分传统产业，逐渐形成了江南沿江技术/资本密集型制造业“中心”和江北沿江劳动密集型制造业“外围”的空间分工格局；（2）江南沿江开发区内部、江北沿江开发区内部尚未形成良好的分工关系；（3）受开发区发展阶段、区域产业政策、本地化资源供给和市场需求等因素影响，并未发现理论预期的普遍存在的产业集聚现象，仅纺织服装、石化、电力、塑料橡胶等产业呈现集中趋势.     

湘北环湖低丘红壤区土壤资源利用：以盘塘实验区为例

以盘塘红壤实验区为例，在阐明湘北环湖低丘红壤区土壤形成、类型及特性的基础上，提出了综合开发利用该区土壤资源的措施和途径。     

The littoral zone of lake okeechobee as a source of phosphorus after drawdown

Following a period of prolonged drought or intentional lake level drawdown, large littoral areas that once contained submersed aquatic vegetation (SAV) are reinundated when lake levels rise. A complete assessment of the contribution made by decomposing SAV to the in-lake phosphorus (P) concentration is important in both the management of Lake Okeechobee and understanding basic P processes. The P contribution to the open waters of Lake Okeechobee from a rapid inundation of exposed SAV was calculated by four methods: cores of field-desiccated SAV, cores of lab-desiccated SAV in the presence and absence of sediments, in situ decomposition, and sequential macrophyte harvesting. P releases, given such an episodic event, were similar among the four methods, ranging from 116±48 to 384±528 mg/m² in the absence of sediment. When SAV is in contact with sediment, which is the realistic field situation, the amount of P released was four times less (30±14 mg/m²) than in the absence of sediment. The calculated P releases would result in total P concentration increases in the lake from 2 to 15 μg/liter (upper 95% CI=2–25 μg/liter) in the absence of sediment; only 1 μg/liter increase was predicted when SAV released P in contact with sediment. Thus it is unlikely that a significant rise in total P concentrations in the limnetic zone of the lake would occur from the export of P released during the desiccation of SAV in the littoral-marsh zone during a drawdown.     

WOODY VEGETATION AND RIPRAP STABILITY ALONG THE SACRAMENTO RIVER MILE 84.5–1191

ABSTRACT: Stability of vegetated and bare riprap revetments along a Sacramento River reach during the flood of record was assessed. Revetment damages resulting from the flood were identified using records provided by the U.S. Army Corps of Engineers and verified by contacts with local interests. Vegetation on revetments along a 35.6-mile reach was mapped using inspection records and stereo interpretation of aerial phoths taken shortly before and after the flood. A follow-up field inspection was conducted in September 1989. Revetment age, material, bank curvature, vegetation, and damage were mapped from a boat. Mapping results from both 1986 and 1989 were placed in a data base. About 70 percent of the bank line of the study reach was revetted. About two-thirds of the revetment was cobble; one-third was quarry stone. Revetment vegetation varied from none to large (> 50-inch diameter) cotton-woods. About 10 percent of the revetted bank line supported some type of woody vegetation. Damage rates for revetments supporting woody vegetation tended to be lower than for unvegetated revetments of the same age located on banks of similar curvature. Chisquared tests indicated damage rates were greater for older (pre-1950 construction) revetments, but were unable to detect differences based on vegetation or bank curvature. Research is needed to generate design criteria and construction techniques to allow routine use of woody plants in bank protection structures.     

Potential coastal impacts of contemporary changing climate on South Asian seas states

The threat of man-induced global change on the nations of the South Asian seas region varies from place to place because of differences in exposure to monsoons and stoms, differences in local tectonics and subsidence, and variations in air and sea climates. Because several nations are involved, some having subsistence budgets, and given the cost of deriving independently a comprehensive response to global change, the similarities and differences between national settings must be identified soon. These comparisons will form the basis for local response strategies: the similarities provide a basis for responses similar to that of other nations and the differences provide for local adaptation. That climate change on the South Asian coastal region will have an impact is certain: its economics, environment, and coastal land uses are dominated to a certain extent by this marine influence. The extent of these impacts, however, is uncertain. Accompanying global change will be changes in sea level, differences in storm climate, and altered precipitation patterns; science cannot define today what pattern these changes will take. Because global change is inevitable—although its magnitude, timing, and geographic distribution are unknown—the South Asian seas region should begin the appropriate research and planning studies to set forth a reasoned response to global change, for implementation when scientific evidence for global change is more quantitative.     

An inventory of wetland impoundments in the coastal zone of Louisiana,USA: Historical trends

We inventoried wetland impoundments in the Louisiana, USA, coastal zone from the late 1900s to 1985. Historically, impoundment of wetlands for reclamation resulted in direct wetland loss after levees (dikes) failed and the impounded area was permanently flooded, reverting not to wetland, but to open-water habitat. A current management approach is to surround wetlands by levees and water control structures, a practice termed semi-impoundment marsh management. The purpose of this semi-impoundment is to retard saltwater intrusion and reduce water level fluctuations in an attempt to reduce wetland loss, which is a serious problem in coastal Louisiana. In order to quantify the total impounded area, we used historic data and high-altitude infrared photography to map coastal impoundments. Our goal was to produce a documented inventory of wetlands intentionally impounded by levees in the coastal zone of Louisiana in order to provide a benchmark for further research. We inventoried 370,658 ha within the coastal zone that had been intentionally impounded before 1985. This area is equal to about 30% of the total wetland area in the coastal zone. Of that total area, approximately 12% (43,000 ha) is no longer impounded (i.e., failed impoundments; levees no longer exist or only remnants remain). Of the 328,000 ha still impounded, about 65% (214,000 ha) is developed (agriculture, aquaculture, urban and industrial development, and contained spoil). The remaining 35% (114,000 ha) of impoundments are in an undeveloped state (wetland or openwater habitat). In December 1985, approximately 50% (78,000 ha) of the undeveloped and failed impoundments were open-water habitat. This inventory will allow researchers to monitor future change in land-water ratios that occur within impounded wetlands and thus to assess the utility of coastal wetland management using impoundments.