海水烟气脱硫及应用前景

SO2已成为世界第一大的大气污染物,它对人类生存的生态环境造成了严重影响,故必须予以脱硫.介绍了海水烟气脱硫工艺的原理、系统及海水脱硫对周围海洋环境的影响和应用前景.     

不同污染程度湖泊沉积物中不同粒级可转化态氮分布

研究了污染程度不同的五里湖、月湖、东太湖和贡湖不同粒级沉积物中总可转化态氮以及各形态可转化态氮的含量与分布.结果表明:4个湖泊的沉积物各粒级中各形态可转化态氮的含量及其地球化学特征均不相同.强氧化剂可提取态氮(SOEF-N)是释放能力最弱的形态,为可转化态氮的主体,占总可转化态氮的66.97%～87.97%.离子交换态氮(IEF-N)结合能力最弱,是最容易被释放的形态,为可转化态无机氮的主体,占总可转化态氮的7.37%～22.25%.同一粒级中,各形态可转化态氮对氮循环的贡献为SOEF-N最大,IEF-N其次,强碱可浸取态氮(SAEF-N)与弱酸可浸取态氮(WAEF-N)最低.随着沉积物粒级的由粗到细,总可转化态氮以及各形态可转化态氮含量均呈逐渐增加趋势.沉积物细颗粒部分对氮循环的可能贡献占绝对的主体,是粗颗粒部分的几倍到几十倍.相比而言,污染程度轻的贡湖和东太湖沉积物无论总可转化态氮还是各形态可转化态氮,细颗粒部分的相对含量均低于污染程度重的五里湖和月湖沉积物.      

PFOS/PFOA环境污染行为与毒性效应及机理研究进展

全氟辛烷磺酰基化合物（PFOS）和全氟辛酸（PFOA）是一类新型的持久性有机污染物（POPs）,近年来发现在环境系统中日益广泛分布,并在生物体内蓄积或发生致毒效应.本文首先从PFOS/PFOA在环境中的污染及其水平、在野生动物体内的暴露、对人体的暴露以及污染与暴露变化趋势等4个方面,分析了PFOS/PFOA最新的环境污染与生物暴露情况;从PFOS/PFOA在大气环境中的转运转化过程、在污水污泥中转运转化过程以及在生物体内的蓄积、代谢转化与降解过程等3个方面,阐述了PFOS/PFOA在环境中的迁移转化行为;还概述了最近几年在PFOS/PFOA所导致的生态效应及其可能的机理研究进展.最后,尝试性地提出了今后在PFOS/PFOA污染生态学方面的研究重点.     

工业废油污染程度的熵权灰色关联模糊评价

在工业废油污染程度综合评价研究中,各类复杂油质和众多影响因素相互作用,各个理化指标间相互联系、相互干扰,因而在评价中存在一些模糊的概念和表象。采用熵权法客观赋权,灰色关联与模糊综合评价相结合的方法建立工业废油污染程度的评价排序模型。根据算例评价结果可知,该方法提供一种新的简便而快捷、适用的评价手段,为选择合适工业废油处理方式,以及工业废油的资源化和环境保护研究提供一定的理论依据。     

A yearly maximum sea level simulator and its applications: A Stockholm case study

A yearly maximum sea level simulator for Stockholm is presented. The simulator combines extreme sea level estimates and mean sea level rise projections into a joint probabilistic framework. The framework can be used, for example, to assess the risk that new structures placed at the current minimum allowed height above the sea level can become flooded in the future. Such assessments can be used to underpin future building free levels, which would be a great improvement over the much more arbitrary criteria in use today. Another strong point of the framework is that it can be used to quantify the influence of uncertainties in mean sea level projections, estimates of sea level extremes and future emission scenarios on the risk of flooding. For Stockholm mean sea level uncertainty is found to be much more important than extreme sea level uncertainty. The framework is also set-up to test adaptation measures. It is found that protections that are built once the mean sea level has risen above some given threshold can be very efficient. Lastly, the framework is embedded into a simple decision problem that can be used to calculate risk/reward ratios for land development as a function of height above today’s mean sea level.     

Predation risk assessment by green frog (<Emphasis Type="Italic">Rana clamitans</Emphasis>) tadpoles through chemical cues produced by multiple prey

Many prey assess predation risk through predator chemical cues. Numerous studies have shown that (1) prey sometimes respond to chemical cues produced by heterospecifics and (2) that many species are capable of associative learning. This study extends this research by focusing on predation risk assessment and antipredator behavior in environments containing chemical cues produced by multiple prey species. The results show that green frog (Rana clamitans) tadpoles (1) assess risk from the chemical cue produced during predation by a heterospecific (gray tree frog, Hyla versicolor, tadpoles) and (2) can exhibit similarly strong behavioral responses to a mix of conspecific and heterospecific cues compared to conspecific cue alone, depending on their conditioning environment. I then discuss how the prey choice of the predators and the relative abundances of the prey species should influence the informational value of heterospecific cues.     

Sea-Cage Aquaculture, Sea Lice, and Declines of Wild Fish

Abstract: A sea cage, sometimes referred to as a net pen, is an enclosure designed to prevent farm fish from escaping and to protect them from large predators, while allowing a free flow of water through the cage to carry away waste. Farm fish thus share water with wild fish, which enables transmission of parasites, such as sea lice, from wild to farm and farm to wild fishes. Sea lice epidemics, together with recently documented population‐level declines of wild salmon in areas of sea‐cage farming, are a reminder that sea‐cage aquaculture is fundamentally different from terrestrial animal culture. The difference is that sea cages protect farm fish from the usual pathogen‐control mechanisms of nature, such as predators, but not from the pathogens themselves. A sea cage thus becomes an unintended pathogen factory. Basic physical theory explains why sea‐cage aquaculture causes sea lice on sympatric wild fish to increase and why increased lice burdens cause wild fish to decline, with extirpation as a real possibility. Theory is important to this issue because slow declines of wild fish can be difficult to detect amid large fluctuations from other causes. The important theoretical concepts are equilibrium, host‐density effect, reservoir‐host effect, and critical stocking level of farmed fish (stocking level at which lice proliferate on farm fish even if wild fish are not present to infect them). I explored these concepts and their implications without mathematics through examples from salmon farming. I also considered whether the lice‐control techniques used by sea‐cage farmers (medication and shortened grow‐out times) are capable of protecting wild fish. Elementary probability showed that (where W is the abundance of wild fish, W* is the prefarm abundance, F is the abundance of farm fish, and is the ratio of lice per farm fish to lice per wild fish). Declines of wild fish can be reduced by short growing cycles for farm fish, medicating farm fish, and keeping farm stocking levels low. Declines can be avoided only by ensuring that wild fish do not share water with farmed fish, either by locating sea cages very far from wild fish or through the use of closed‐containment aquaculture systems. These principles are likely to govern any aquaculture system where cage‐protected farm hosts and sympatric wild hosts have a common parasite with a direct life cycle.     

Experimental investigation of bubbly flow and turbulence in hydraulic jumps

Many environmental problems are linked to multiphase flows encompassing ecological issues, chemical processes and mixing or diffusion, with applications in different engineering fields. The transition from a supercritical flow to a subcritical motion constitutes a hydraulic jump. This flow regime is characterised by strong interactions between turbulence, free surface and air–water mixing. Although a hydraulic jump contributes to some dissipation of the flow kinetic energy, it is also associated with increases of turbulent shear stresses and the development of turbulent eddies with implications in terms of scour, erosion and sediment transport. Despite a number of experimental, theoretical and numerical studies, there is a lack of knowledge concerning the physical mechanisms involved in the diffusion and air–water mixing processes within hydraulic jumps, as well as on the interaction between the free-surface and turbulence. New experimental investigations were undertaken in hydraulic jumps with Froude numbers up to Fr = 8.3. Two-phase flow measurements were performed with phase-detection conductivity probes. Basic results related to the distributions of void fraction, bubble frequency and mean bubble chord length are presented. New developments are discussed for the interfacial bubble velocities and their fluctuations, characterizing the turbulence level and integral time scales of turbulence representing a “lifetime” of the longitudinal bubbly flow structures. The analyses show good agreement with previous studies in terms of the vertical profiles of void fraction, bubble frequency and mean bubble chord length. The dimensionless distributions of interfacial velocities compared favourably with wall-jet equations. Measurements showed high turbulence levels. Turbulence time scales were found to be dependent on the distance downstream of the toe as well as on the distance to the bottom showing the importance of the lower (channel bed) and upper (free surface) boundary conditions on the turbulence structure.     

A SIPHON GAGE FOR MONITORING SURFACE-WATER LEVELS1

A device that uses a siphon tube to establish a hydraulic connection between the bottom of an onshore standpipe and a point at the bottom of a water body was designed and tested for monitoring surface-water levels. Water is added to the standpipe to a level sufficient to drive a complete slug of water through the siphoning tube and to flush all air out of the system. The water levels in the standpipe and the water body equilibrate and provide a measurable static water surface in the standpipe. The siphon gage was designed to allow quick and accurate year-round measurements with minimal maintenance. Currently available devices for monitoring surface-water levels commonly involve time-consuming and costly installation and surveying, and the movement of reference points and the presence of ice cover in cold regions cause discontinuity and inaccuracy in the data collected. Installation and field testing of a siphon gage using 0.75-in-diameter polyethylene tubing at Ashumet Pond in Falmouth, Massachusetts, demonstrated that the siphon gage can provide long-term data with a field effort and accuracy equivalent to measurement of ground-water levels at an observation well.     

PCBs contributions to the total TEQ released from Korean municipal and industrial waste incinerators

Non-ortho and mono-ortho polychlorinated biphenyls (PCBs) were determined in the stack gases and the fly-ash from nine Korean municipal solid waste incinerators (MSWIs). Soil samples collected near MSWI and industrial waste incinerator (IWI) sites were also examined for PCBs. The PCBs levels in the stack gas samples ranged between 0.0046 and 12.0 TEQ-ng/Nm³. The PCB homologue profiles were distinct for the stack gas samples and different from the fly-ash. PCBs levels in soil samples collected near MSWIs and IWI ranged between 0.86 and 19.73 TEQ-ng/g with background levels of 0.17 TEQ-ng/g. The lower chlorination PCBs were dominant in the soil samples. The stack emission PCBs homologue patterns were compared to those detected in the soil samples. The findings suggest that localized point sources as well air mass movement contribute to the deposition of PCBs onto soil.