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561.
渤海的辽东湾是世界上典型的海湾结冰区,位于冰区中的石油平台油轮外输作业中,流冰连续不断地漂移、聚集形成堆积冰,给海上油轮的外输作业安全带来严重危害。本文概述了在国内首次利用船载雷达,在该湾冰区石油平台上,现场采用雷达海冰监测预报技术系统,进行遥感海冰数据源的获取,图像的解译和数值化处理,得到流冰类型、冰厚度、流冰密集度、流冰速度、方向、流冰漂移轨迹等要素。同时首次现场实时计算出雷达冰漂流场矢量图,并开展了雷达海冰数值跟踪预报,在冰区油轮外输作业中得到很好应用,为雷达技术对水体和海冰监测和预报、遥感应用新领域提供科学依据。 相似文献
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Functional microorganisms to high concentration phenol containing Cr^6+ and Pb^2+ were cultured and biofilm was formed on polypropylene packings in bioelectro-reactor. It was found that the biodegradation capability of such biofilm to phenol changed with the applied voltage. Under the optimal electric field conditions (voltage of 3.0 V, electric field of strength 17.7 V/m and current density of 1.98 A/m2), biodegradation efficiency of phenol aof concentration of 1200 mg/L increased 33% compared to the instance without applying electric field. However, voltage had inverse effect on biodegradation, as microorganisms were killed under strong electric field. Voltage had little effect on heavy ions elimination. Higher absorption rate of Cr^6+ and Pb^2+ was observed when changing pH fi'om acidic to neutral. The experiment results indicated that, after treatment, 10 L phenol of 2400 mg/L was biodegraded completely within 55 h and concentrations of Cr^6+ and Pb^2+ dropped to less than 1 mg/L within 12 h and 6 h, fi'om initial values of 50 mg/L and 30 mg/L, respectively. 相似文献
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提出了强风环境非平稳风速分析模型。该模型将风速记录分解为时变平均风和零均值平稳脉动风分量两部分,给出了经验模型法确定时变平均风的步骤并重新定义了风特性参数的计算公式。分别采用非平稳和平稳风速模型进行了1 851小时实测强风资料的风特性参数计算并做了对比分析。结果显示非平稳模型计算得到的紊流强度和积分尺度较平稳模型小,而平均风速及相干函数的衰减系数则相当接近,非平稳模型较平稳模型更适合描述强风特性。 相似文献
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为了解决目前隧道施工过程中掌子面开挖爆破产生的冲击波容易造成工程灾害的问题,基于宁攀高速胜利隧道台阶法开挖的实际情况,采用动力分析软件ANSYS/LS-DYNA及现场测试的方法研究冲击波在隧道上下台阶区段的传播规律。研究结果表明:初始冲击波传播至下台阶断面时先扩散至中上区域,与拱顶及侧壁碰撞反射后再传播至下部区域;冲击波在下台阶段0~10 m范围内,经多次反射叠加形成提升幅度约30%的第2次超压峰值;冲击波由上台阶较小断面进入下台阶较大断面传播时,超压衰减速度相对加快,过渡界面前后10 m范围内衰减系数由1.01%最高提升至1.05%。现场实测数据与数值模拟结果在上下台阶段得到的波形传播规律基本一致,验证数值模拟的可靠性。研究结果可为实际工程中爆破冲击波在变截面隧道中的控制措施提供参考。 相似文献
566.
Gupta I Dhage S Jacob N Navada SV Kumar R 《Environmental monitoring and assessment》2006,114(1-3):199-209
The city of Mumbai, India with a population of 15 million discharges about 2225 MLD of domestic wastewater after partial treatment to adjoining marine water body. Under the Mumbai Sewage Disposal Project Scheme, sewage is being disposed to the west coast at Worli and Bandra through 3.4 kms long submarine outfalls. A field study was conducted at recently commissioned outfall diffuser location at Worli, at the onset of neap flood tide to study the dispersion patterns and measure the far field dilutions using radio and dye tracers. Estimated dilutions using different tracers were compared with outputs from an empirical model (Brooks) and a 2D numerical model (DIVAST). Validation using parameters such as BOD and FC, indicated a good match for BOD in near field compared to FC. The radiotracer 82Br and Rhodamine WT generally gave good correlation with Brooks' and DIVAST models for nearfield, however at further distances predictions were not accurate. 相似文献
567.
Within the European intensive forest monitoring programme, the native vegetation on permanent Level II plots has been monitored for visible ozone injuries. The main purpose of the programme is to assess the potential risks for the forest vegetation and the natural ecosystems at the intensive monitoring plots. During the first years of the programme the surveys were qualitative, reporting only the number and the name of the symptomatic species in selected Light Exposed Sampling Site. In 2003 a new plot design was tested, based on the distribution of a number of miniplots along the edge of the forest, so as to obtain quantitative findings about the occurrence and distribution of the symptoms. The problems that still persist are related to: (i) the forest edge assessed for ozone symptoms may have a different floristic composition from the Level II plot itself; (ii) the anthropic pressure and the disturbances affecting the forest edge alters the floristic composition; (iii) the variability of the plant composition in the forest edge, which makes comparability difficult between different sites; and (iv) the evaluation of symptoms in several species that have not yet been experimentally tested. Further difficulties are due to the fact that symptoms observed in the field are often aspecific and cannot, therefore, be attributed solely to the phytotoxic action of ozone. To improve the effectiveness of the European programme, it is necessary: (i) to individualise and select common sensitive plant species for homogeneous ecological regions; (ii) to enhance experimental activities to test the sensitivity of a large number of plant species. 相似文献
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