P2P防污染机制的研究

文件污染是当前P2P文件共享系统普遍存在的问题,其中用户行为是导致污染的重要因素.在考察用户行为的基础上,建立了一个污染文件传播模型,描述了用户的污染意识、共享倾向等因素对污染传播的影响,并据此提出了相应的反污染机制.仿真实验表明,该机制能够有效地控制P2P文件共享系统中污染文件的传播.图6,表12.     

基于P2P的网络即时通讯模式

介绍了对P2P网络技术的概念和特点．并对即时通讯工具的广泛应用及其发展中遇到的瓶颈进行了阐述,在综合分析的基础上提出了P2P技术在即时通讯中应用的三种模式：分布式、集中式、混合式．图3,参4．     

布鲁姆过滤器算法在P2P系统中的应用

布鲁姆过滤器算法是一类空间效率和时间效率均较高的查询算法,被广泛地应用于各类分布式数据库及分布式网络系统中,如P2P系统.文中分析了P2P技术在互联网中的应用实例,总结了布鲁姆过滤器算法在P2P系统中的主要应用,如数据同步、资源路由、关键字检索等.     

Ecotoxicological risks of the abandoned F–Ba–Pb–Zn mining area of Osor (Spain)

Due to its potential toxic properties, metal mobilization is of major concern in areas surrounding Pb–Zn mines. In the present study, metal contents and toxicity of soils, aqueous extracts from soils and mine drainage waters from an abandoned F–Ba–Pb–Zn mining area in Osor (Girona, NE Spain) were evaluated through chemical extractions and ecotoxicity bioassays. Toxicity assessment in the terrestrial compartment included lethal and sublethal endpoints on earthworms Eisenia fetida, arthropods Folsomia candida and several plant species, whereas aquatic tests involved bacteria Vibrio fischeri, microalgae Raphidocelis subcapitata and crustaceans Daphnia magna. Total concentrations of Ba (250–5110 mg kg^?1), Pb (940 to >5000 mg kg^?1) and Zn (2370–11,300 mg kg^?1) in soils exceeded intervention values to protect human health. Risks for the aquatic compartment were identified in the release of drainage waters and in the potential leaching and runoff of metals from contaminated soils, with Cd (1.98–9.15 µg L^?1), Pb (2.11–326 µg L^?1) and Zn (280–2900 µg L^?1) concentrations in filtered water samples surpassing US EPA Water Quality Criteria (2016a, b). Terrestrial ecotoxicity tests were in accordance with metal quantifications and identified the most polluted soil as the most toxic. Avoidance and reproduction tests with earthworms showed the highest sensitivity to metal contamination. Aquatic bioassays performed in aqueous extracts from soils confirmed the results from terrestrial tests and also detected toxic effects caused by the mine drainage waters. Algal growth inhibition was the most sensitive aquatic endpoint. In view of the results, the application of a containment or remediative procedure in the area is encouraged.     

P肥施入土壤后的变化进程及对P淋失的影响

对施入不同剂量P肥的稻田土壤进行培养,测定不同时期土壤O lsen-P和CaC l2-P含量变化。结果表明,在施P量为100~1 600 kg.hm-2条件下,200 d时不同处理土壤O lsen-P含量降低量均接近于施P后的50%,不同施P量下土壤对O lsen-P的固定量均接近50%,表明在本试验施P量范围内该土壤仍未达到P吸附饱和,土壤对O lsen-P的固定量与施P量近似呈正比;当施P量低时,CaC l2-P含量低,且变化不明显;当施P量高于400 kg.hm-2时,CaC l2-P含量迅速增高。随着施P量提高,进入土壤缓效P库的比例降低,而进入速效P库和可溶性P库的比例增加,土壤对P的固定能力也逐渐降低,产生P损失的可能性增加,易于导致面源污染。预测结果表明,该土壤发生P素地表径流损失及在亚表层径流中P浓度猛增的O lsen-P含量“转折点”为81.3 mg.kg-1,与其对应的施P量约为524 kg.hm-2。可见,该土壤施P量一旦高于500 kg.hm-2,通过各种途径产生P损失的可能性增加。     

Numerical study of wave–current–vegetation interaction in coastal waters

Research on interactions among wave, current, and vegetation has received increasing attention. An explicit depth-averaged hydrodynamic model coupled with a wave spectral model (CMS-wave) was proposed in this study in order to simulate the wave and wave-induced current in coastal waters. The hydrodynamic model was based on the finite volume method while the intercell flux was computed by employing the Harten–Lax–van Leer approximate Riemann solver to investigate the dry-to-wet interface, and the drag force of vegetation was modeled as the sink terms in the momentum equations. The CMS-wave model was used to investigate the non-breaking and the breaking random waves propagation in vegetation fields. Afterwards, an empirical wave energy dissipation term with plant effect was derived to represent the resistance induced by aquatic vegetation in the wave-action balance equation. The established model was calibrated and validated with both the experimental and field data. The results showed that the wave height decreased significantly along the wave propagation direction in the presence of vegetations. The sensitivity analysis for the plant density, the wave height, and the water depth were performed by comparing the numerical results for the wave height attenuation. In addition, wave and wave-induced current through a finite patch of vegetation in the surf zone were investigated as well. The strong radiation stress gradient could be produced due to the variation of the energy dissipation by vegetation effect in the nearshore zone, which impacted the direction and amplitude of the longshore current. The calculated results showed that the coupling model had good performance in predicting wave propagation and the current over vegetated water regions.     

Predator–prey fuzzy model

In this work we have used fuzzy rule-based systems to elaborate a predator–prey type of model to study the interaction between aphids (preys) and ladybugs (predators) in citriculture, where the aphids are considered as transmitter agents of the Citrus Sudden Death (CSD). Simulations were performed and a graph was drawn to show the prey population, the potentiality of the predators, and a phase-plane. From this phase-plane, a classic model of the Holling–Tanner type is fitted and its parameters were found. Finally, we have studied the stability of the critical points of the Holling–Tanner model.     

Evaluating poverty–environment dynamics

Developing indicators to more effectively evaluate poverty–environment dynamics and inform policy is an urgent research priority. It is critical that these indicators are used in ways that accurately represent the relationship they are meant to inform. This article evaluates the theory and use of poverty–environment indicators, a relatively new tool developed to aid in the design and evaluation of poverty reduction strategies in the context of environmental change. We argue that while they have great potential, in their current form and use, poverty–environment indicators may contribute to critical misunderstandings of processes on the ground. These issues stem from a problematic and largely unacknowledged process of simplifying particular poverty–environment relationships. This article lays out the problematic character of this simplification process, and suggests how we might address these problems to create more useful understandings of poverty–environment dynamics to inform policy.     

应用Casio fx-3600P(fx-180P)计算器计算中位数和平均差的方法

在统计学上,对试验和观察所获得的数据,常用中位数和平均差作为偏态分布的资料特征数。计算平均差要算出频数和离差绝对值的乘积(fi|xi|)。当分组数据较多时,应用Casio fx—3600P(fx—180P)计算器程序,先把xi最小值独立储存,把fi|xi|累加,并利用选择正负的语句分别计算储存乘积。此法较为迅捷、准确。     

应用Casiofx—3600P（fx—180P）计算器计算中位数和平均差的方法

在统计学上，对试验和观察所获得的数据，常用中位数和平均差作为偏态分布的资料特征数，计算平均差要算出频数秘离差绝对值的乘积（fi|xi|)，当分组数据较多时，应用Casiofx-3600P(fx-180P)计算器程序，先把xi最小值独立储存，把fi|xi|累加，并利用选择正负的语句分别计算储存乘积，此法较为迅速，准确。     

Update of intensity–duration–frequency curves for Kuwait due to extreme flash floods

Environmental and Ecological Statistics - Flash floods have devastating power due to their high rainfall intensities and short durations, causing serious damage to infrastructure and human life....     

Dimethylsulphide and ocean–atmosphere interactions

Dimethylsulphide (DMS) is a trace sulphur gas found in most atmospheric and surface water samples, which is derived from dimethylsulphonioproprionate (DMSP). Although it has been extensively studied over the last 50 years, its natural production, consumption and cycling are still not completely understood. Until recently, DMS was believed to originate mainly from marine waters, but later studies have shown that estuaries and lakes are also an important source of DMS. DMS also originates from terrestrial plants such as maize, wheat and lichen, but it is not fully understood why. DMS is believed to have an important impact on the global environment by influencing factors such as the acidity of the atmosphere, cloud condensation nuclei (CNN) and solar insolation. The impact that humans have on the cycling of DMS and on its environmental impact is not well understood either. DMS is affected by temporal and geographical factors, as well as physical factors such as salinity and wind speed, yet when studied under El Niño conditions which modify these physical factors in vivo, there was found to be no fluctuation in the concentration of DMS in the water column. This review outlines our current state of knowledge on DMS.     

Simulations of the flow in the Mahakam river–lake–delta system,Indonesia

Large rivers often present a river–lake–delta system, with a wide range of temporal and spatial scales of the flow due to the combined effects of human activities and various natural factors, e.g., river discharge, tides, climatic variability, droughts, floods. Numerical models that allow for simulating the flow in these river–lake–delta systems are essential to study them and predict their evolution under the impact of various forcings. This is because they provide information that cannot be easily measured with sufficient temporal and spatial detail. In this study, we combine one-dimensional sectional-averaged (1D) and two-dimensional depth-averaged (2D) models, in the framework of the finite element model SLIM, to simulate the flow in the Mahakam river–lake–delta system (Indonesia). The 1D model representing the Mahakam River and four tributaries is coupled to the 2D unstructured mesh model implemented on the Mahakam Delta, the adjacent Makassar Strait, and three lakes in the central part of the river catchment. Using observations of water elevation at five stations, the bottom friction for river and tributaries, lakes, delta, and adjacent coastal zone is calibrated. Next, the model is validated using another period of observations of water elevation, flow velocity, and water discharge at various stations. Several criteria are implemented to assess the quality of the simulations, and a good agreement between simulations and observations is achieved in both calibration and validation stages. Different aspects of the flow, i.e., the division of water at two bifurcations in the delta, the effects of the lakes on the flow in the lower part of the system, the area of tidal propagation, are also quantified and discussed.     

Efficient implementation of the Metropolis-Hastings algorithm,with application to the Cormack–Jolly–Seber model

Judicious choice of candidate generating distributions improves efficiency of the Metropolis-Hastings algorithm. In Bayesian applications, it is sometimes possible to identify an approximation to the target posterior distribution; this approximate posterior distribution is a good choice for candidate generation. These observations are applied to analysis of the Cormack–Jolly–Seber model and its extensions.     

The spider and fly revisited: ploy–counterploy behavior in a unique predator–prey system

Earlier studies have shown that the sarcophagid fly Arachnidomyia lindae is the principal egg-sac predator of the colonial orb-weaving spider Metepeira incrassata, and that risk of egg-sac loss increases with group size. Observations of specialized behaviors for attack (flies) and defense (spiders) suggest that this predator-prey relationship may incorporate elements of ploy and counterploy behavior. Here we explore this relationship in detail and test hypotheses regarding efficacy of attack and defense behaviors. Egg-sac guarding by the spider includes defensive behaviors specific to this fly predator, which were observed during experimental "attacks" with tethered A. lindae, but not with similar presentations of non-predatory Musca domestica. Experimental studies also show that Metepeira incrassata recognizes this predatory fly by airborne cues (i.e., the signature frequency of wing-beats), and can distinguish between this predator and other flies (potential prey) on the basis of wing-beat frequency differences. Removal of female spiders results in a significantly higher probability of unguarded egg-sacs being parasitized, demonstrating the adaptive value of spider defensive behaviors. We also present evidence that A. lindae utilizes a behavioral ploy for circumventing spider guarding behavior (aggressive mimicry - producing vibrations of captured prey in the web), and that Metepeira incrassata, in turn, exhibits a counter-ploy behavior (signal thread cutting) to eliminate this potentially distracting vibratory information. While previous studies have shown that this colonial web-building spider uses a number of general attack-abatement mechanisms against a diversity of predators and parasitoids, results of this study suggest that selection pressures from a highly specialized predator may also result in evolution of predator-specific prey responses.     

^32P后标记方法测DNA加合物

用~(32)P后标记的方法测DNA和环氧苯乙烯体外反应的加合物,是将小牛胸腺DNA和环氧苯乙烯仿照体内条件进行体外反应,反应产物在核酸内切酶及外切酶的存在下,水解成2’-脱氧核糖核苷3’-单磷酸(dNmP).这种水解后的3’-单磷酸在T_4多核激酶的存在下,使γ~(32)P ATP上的放射磷与核苷的磷进行交换反应,生成2’-脱氧核苷-3’,5’-二磷酸(dNDP).被标记的3’,5’-二磷酸及加合物,通过ODS薄层色谱板及PEI纤维阴离子交换色谱板进行适当的分离分辨分析,使DNA加合物从正常的核酸分子中分离出来.用自显影加上空白对照确定加合物的指纹图,最后用液体闪烁计数要定量分析DNA加合物的量。 用这种方法测DNA和环氧苯乙烯体外反应加合物,在自显影指纹图上发现5种多余的斑点,初步确定是DNA的5种加合物或加合物的衍生物.它们的修饰点是鸟嘌呤上的N-7,N-2,O~6位,修饰量在本实验的条件下是1加合物/10~4—6正常核酸.同时用这种方法测动物活细胞和环氧苯乙烯修饰反应产物,发现有DNA加合物存在.在职业接触苯乙烯工人静脉血中也发现有DNA-环氧苯乙烯的加合物,测定结果其样品指纹图与体外反应DNA指纹图类似. ~(32)P后标记方法是灵敏的,最高可侧到1加合物/10~(10)—11正常核酸,这已接近二倍体细胞的基因水平,是当今测DNA加合物方法中最     

^32P后标记法测DNA加合物

＾３２Ｐ后标记方法测ＤＮＡ－致癌物的加合物过程是用小球菌核酸酶和脾核酸酶将ＤＮＡ及加合物酶解成２′－脱氧核苷３′－单磷酸（３′－ｄＮｍＰ＋３′－ｄｘｍＰ）,以它为底物,用Ｔ４多核苷酸激酶催化,使γ＾３２ＰＡＴＰ的放射＾３２Ｐ转移反应到底物上,形成２′－脱氧核苷３′５′．ｄＮＤＰ＋３′５′＊ｄｘＤＰ）,用ＯＤＳ－ＴＬＣ和ＰＥＩ－ＴＬＣ结合将标记过的二磷酸分离分辨,用自显影制成加合物的指纹图,液闪计数     

Chemical and isotopic composition of CO2-rich magnesium–sodium–bicarbonate–sulphate-type mineral waters from volcanoclastic aquifer in Rogaška Slatina,Slovenia

Environmental Geochemistry and Health - Bottled natural mineral waters from an andesitic aquifer in Slovenia are enriched in magnesium (1.1 g/l), sulphate (2.2 g/l) and dissolved...