The Shallow‐Water Component of the Chesapeake Bay Environmental Model Package

The shallow‐water component of the Chesapeake Bay Environmental Model Package emphasizes the regions of the system inside the 2‐m depth contour. The model of these regions is unified with the system‐wide model but places emphasis on locally significant components and processes, notably submerged aquatic vegetation (SAV), sediment resuspension, and their interaction with light attenuation (Ke). The SAV model is found to be most suited for computing the equilibrium distribution of perennial species. Addition of plant structure and propagation are recommended to improve representation of observed trends in SAV area. Two approaches are taken to examining shallow‐water Ke. The first compares observed and computed differences between deep‐ and shallow‐water Ke. No consistent difference in observations is noted. In the preponderance of regions examined, computed shallow‐water Ke exceeds computed deep‐water Ke. The second approach directly compares Ke measured in shallow water with modeled results. Model values are primarily lower than observed, in contrast to results in deep water where model values exceed observed. The shortfall in computed Ke mirrors a similar shortfall in computed suspended solids. Improved model representation of Ke requires process‐based investigations into suspended solids dynamics as well as increased model resolution in shallow‐water regions.     

SMBR法处理印染废水的膜污染减缓方法研究

针对SMBR法处理印染废水膜污染进行研究,从减缓膜污染的角度出发,通过实验得到了针对实验系统的膜污染的几个影响因素,确定了系统的临界压力和临界通量,并证明在临界压力和通量下膜污染明显减缓;膜组件倾斜于30°放置,压力增长缓慢;系统在临界压力0.015 MPa左右进行空曝气时,膜通量恢复了43%。     

水生维管束植物在修复受损水环境中的选择与配置

水生维管柬植物通过对污染物的吸收、富集,与藻类的竞争或他感抑制作用以及根际水生生态系统的协同作用等方式实现对受损水环境的修复,是一种与建设污水处理厂互补的水环境修复技术。着重指出利用水生维管束植物在修复受损水环境应用中的科学选择与配置,尤其是应优先考虑选择少量先锋物种,以便尽快恢复水环境生态系统的基本结构和功能以及生物多样性;重视各种生活型水生植物的合理搭配,优势互补,稳定有效地发挥各自的生态功能;注意考虑水生植物种群配置在生长期上的密切衔接及群落优势中的季节性演替等;并佐以实例为实际应用提供参考。     

Zeolite powder addition to improve the performance of submerged gravitation-filtration membrane bioreactor

In this study, the effect of zeolite powder addition on submerged membrane bioreactor （SMBR） on membrane permeability, and the removals for COD, NH3-N, TN were investigated. Through the parallel operation of control and test systems, it was found that the zeolite powder addition could alleviate the ultra-filtration membrane fouling and enhance the membrane permeability. On the basis of experimental investigations, a concept of ＂protection coating layer＂ was proposed to illustrate the phenomenon of UF membrane fouling. In addition, the removal for COD in test system was more stable, a little higher compared to the control system. Due to the combination of nitrification and ion exchange, a more excellent removal for NH3-N in test system was obtained regardless of influent NH3-N loading rate. It was also found that a mean 25% higher TN removal took place in the test system, and ion exchange and simultaneous nitrification and de-nitrification were analyzed to be main factors. During the stable operation period, the SOURs of test zeolite powder added sludge and control activated sludge were measured to be 75 mgO2/（gMLVSS, h） and 24 mgO2/（gMLVSS, h） respectively, it meant that the zeolite powder addition could enhance the microorganism activity significantly.     

非自愿性移民生产安置中土地公平补偿研究——以湖南皂市水利枢纽工程为例

水利水电工程建设与移民安置会占用淹没区与安置区土地,根据补偿原理,淹没区与安置区理应获得补偿,从公平角度研究其土地补偿,对于增进移民与安置区居民福祉、实现社会公平正义具有积极意义。本文在界定和讨论淹没区与安置区土地公平补偿内涵与范围的基础上,分析了研究区域现行补偿标准的公平性,采用收益还原法和条件价值法分别测算了淹没区与安置区土地的市场价值与非市场价值,并由此测算土地公平补偿。结果表明:1淹没区与安置区土地公平补偿内涵是"损失什么,补偿什么",采取完全补偿原则,能体现"两区"之间的公平,公平补偿范围包括农地市场价值和非市场价值;2研究区域淹没区和安置区水田的市场价值分别是698 558.18元/hm2和573 272.73元/hm2,旱地为457 090.91元/hm2和465 818.18元/hm2;淹没区和安置区水田的非市场价值为50 006.40元/hm2和52 008.36元/hm2,旱地为47 045.65元/hm2和48 278.08元/hm2。3淹没区水田公平补偿测算结果为748 564.58元/hm2,旱地为504 136.56元/hm2;安置区水田公平补偿为625 281.09元/hm2,旱地为514 096.26元/hm2;4现行淹没区水田和旱地补偿标准仅为测算结果的53.77%和53.80%,安置区的补偿标准更是远低于该测算结果。研究结论:研究区域现行土地补偿标准仅能反映部分农地价值,是不完全补偿,同时,有关补偿制度未将淹没区与安置区土地补偿置于平等地位,现行土地补偿标准有失公平;本文基于农户的福利损失测算土地补偿,体现了公平补偿内涵;在土地补偿政策改进方面,应提高淹没区与安置区土地补偿标准,建立完善的社会保障制度,实施更加积极的就业政策等。     

Arsenic accumulation and translocation in the submerged macrophyte Hydrilla verticillata (L.f.) Royle

Worldwide contamination of arsenic in aquatic systems requires the development of a cost-effective, in situ phytoremediation technology. Hydrilla verticillata (L.f.) Royle, a submerged macrophyte widely distributed throughout the world, has the potential to effectively remove heavy metals from water. In order to understand the potential of H. verticillata for As phytofiltration and its impacts on As cycling in the water system, we investigated As accumulation, speciation and translocation in H. verticillata plants. Plant shoots showed a significant accumulation of As, with a maximum of >700 μg g⁻¹ dry weight (DW) after exposure to 20 μM arsenate [As(V)] or arsenite [As(III)] for 4 d, with no significant differences between the As(V) and As(III) treatments (P > 0.05). In addition, results of an in planta transport experiment showed that, after exposure of root and shoot to 2 μM As(V) and As(III) for 4 d, the bioconcentration factor (BCF) in roots for As(V) was almost twofold than that of As(III). Higher As BCFs in roots compared to shoots was also observed. Arsenic accumulated primarily in the cell walls of root cells (>73% of the total As in roots) and in the soluble parts of leaves (>60% of the total As in leaves). Regardless of the form of As supplied [As(III) or As(V)], As(V) was the dominant form in roots and As(III) was the dominant form in leaves. Further, basipetal translocation of As in this plant (?17%) was markedly higher than acropetal translocation (?3%). Because of accumulation of As in the shoot and immobilization of As below ground in roots, H. verticillata is a potential As phytofiltrator for bioremediation.     

Aquatic arsenic: phytoremediation using floating macrophytes

Phytoremediation, a plant based green technology, has received increasing attention after the discovery of hyperaccumulating plants which are able to accumulate, translocate, and concentrate high amount of certain toxic elements in their above-ground/harvestable parts. Phytoremediation includes several processes namely, phytoextraction, phytodegradation, rhizofiltration, phytostabilization and phytovolatilization. Both terrestrial and aquatic plants have been tested to remediate contaminated soils and waters, respectively. A number of aquatic plant species have been investigated for the remediation of toxic contaminants such as As, Zn, Cd, Cu, Pb, Cr, Hg, etc. Arsenic, one of the deadly toxic elements, is widely distributed in the aquatic systems as a result of mineral dissolution from volcanic or sedimentary rocks as well as from the dilution of geothermal waters. In addition, the agricultural and industrial effluent discharges are also considered for arsenic contamination in natural waters. Some aquatic plants have been reported to accumulate high level of arsenic from contaminated water. Water hyacinth (Eichhornia crassipes), duckweeds (Lemna gibba, Lemna minor, Spirodela polyrhiza), water spinach (Ipomoea aquatica), water ferns (Azolla caroliniana, Azolla filiculoides, and Azolla pinnata), water cabbage (Pistia stratiotes), hydrilla (Hydrilla verticillata) and watercress (Lepidium sativum) have been studied to investigate their arsenic uptake ability and mechanisms, and to evaluate their potential in phytoremediation technology. It has been suggested that the aquatic macrophytes would be potential for arsenic phytoremediation, and this paper reviews up to date knowledge on arsenic phytoremediation by common aquatic macrophytes.     

生物陶粒柱—PAC—膜过滤装置系统处理饮用水实验研究

生物陶粒柱和粉末活性炭作为淹没式中空纤维膜过滤装置的预处理工艺不仅解决了膜过滤装置氨氮去除不利的弱点,避免了亚硝酸盐氮的积累,而且在浊度、细菌、有机物等方面极大地降低了膜过滤装置的负荷。生物陶粒柱－PAC－膜过滤装置系统高锰酸盐指数平均去除率为76．97％,氨氮和亚硝酸盐氮的平均去除率分别达到顾95．50％和99．15％。     

淹没复合式膜生物反应器技术

综述了膜生物反应器技术进展并分析,阐述了其优特点,提出了新型的淹没复合式膜生物反应器（SHMBR）以及用于污水处理和回用的工艺,从水处理工艺学,流体力学,水微生物学方面论述了其所具的特点,说明了淹没复合式膜生物反应器是一种高效,低耗,资源化的污水生物反应器,指出了今后需研究的问题。