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氧化镁湿法烟气脱硫技术已在我国推广应用,在氧化镁湿法烟气脱硫工艺中,关健设备是吸收塔.以2×300 MW机组烟气脱硫工程为例,对吸收塔本体结构尺寸进行设计及选型,为镁法脱硫吸收塔设计提供参考. 相似文献
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湿法烟气脱硫吸收塔系统的设计和运行分析 总被引:16,自引:0,他引:16
详细介绍了广东省连州电厂石灰石/石膏湿法烟气脱硫吸收塔系统的流程,设备,吸收塔内部结构、防腐措施等设计情况,同时对系统的运行状况进行了分析。 相似文献
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氨法脱硫副产物亚硫酸铵的塔外氧化 总被引:2,自引:0,他引:2
根据氨法脱硫反应机理,提出了将脱硫生成的亚硫酸铵溶液排放到吸收塔外进行氧化的方法,一方面可以减少脱硫塔的注氨量,有效控制吸收塔出口烟气中的逸氨及硫酸铵气溶胶,避免二次污染;另一方面,可以提高吸收塔内亚硫酸铵浓度,保持较高的脱硫率.塔外氧化对于氨法脱硫是一种比较合理的氧化方法. 相似文献
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吸收塔浆液起泡原因分析及消泡剂的选择 总被引:1,自引:0,他引:1
针对在多个湿法脱硫项目中出现的吸收塔浆液起泡现象,分析了引起塔内浆液起泡的原因,提出了相应的处理措施,探讨脱硫吸收塔浆液起泡专用消泡剂的作用原理及选择原则。 相似文献
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烟气脱硫吸收塔总体结构计算方法 总被引:1,自引:0,他引:1
研究了火电厂烟气脱硫吸收塔总体结构,分析了吸收塔各种荷载对结构计算的影响,运用国内有关标准规范计算吸收塔壳体厚度,为脱硫行业吸收塔的总体结构计算提供参考。 相似文献
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吸收塔是火电厂烟气脱硫装置中的关键设备,以铜陵电厂2×1 000MW机组烟气脱硫装置吸收塔安装为例,介绍了吸收塔倒装工艺及其特点。由于倒装法在降低费用、缩短工期、减少高空作业量、不受场地限制等方面具有显著的优点,因而在吸收塔的施工技术中被广泛采用。 相似文献
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介绍了烟气脱硫系统中三种主要的吸收塔类型,及烟气在吸收塔中停留时间和喷淋吸收区高度的计算方法。简述了液气比与气速、烟气中SO2含量的关系,并列举了喷淋塔、动力波塔和平流塔等工程实例。 相似文献
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脱硫系统的发生的故障主要是吸收塔系统出现的异常工况,分析吸收塔系统浆液循环泵叶轮磨损、浆液泵出口母管堵塞、吸收塔内浆液异常等对吸收塔出口参数的影响,并提出了各种异常现象发生时的解决方法,为减少脱硫系统故障,确保烟气达标排放提供参考。 相似文献
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Pradeep Jain Timothy G. Townsend Thabet M. Tolaymat 《Waste management (New York, N.Y.)》2010,30(11):2022-2029
The rate at which liquids can be added to a vertical well, the lateral zone of impact of the well, and the liquids volume needed to wet the waste within the zone of impact of the well are the key inputs needed to design a vertical well system. This paper presents design charts that can be used to estimate these inputs as a function of municipal solid waste properties (porosity, hydraulic conductivity, and anisotropy ratio), well dimensions (radius and screen length), and injection pressure. SEEP/W modeling was conducted to estimate the key design inputs for a range of conditions practically encountered for a vertical well installed in landfilled waste. The flow rate, lateral zone of impact of a well, liquids volume added, and injection pressure were normalized with the waste properties and well dimensions to formulate dimensionless variables. A series of design charts were created to present dimensionless steady-state flow rate, lateral zone of impact, and the dimensionless liquid volume needed to reach a steady-state condition, as a function of dimensionless input variables. By using dimensionless variables formulated for this work, these charts permit the user to estimate the steady-state design variables described above for a wide range of configurations and conditions beyond those simulated without the need for further modeling. The results of the study suggest that the lateral extent of the well can be estimated using Darcy’s equation and assuming saturated unit-gradient vertical flow regime below the well bottom. An example problem is presented to illustrate the use of the design charts. The scenario described in the example problem was also modeled with SEEP/W, and the results were compared with those obtained from the design charts to demonstrate the validity of design charts for scenarios other than those used for the development of the design charts. The methodology presented in this paper should be thought of as a means to provide a set of bounds that an engineer can use along with their judgment in the design of a system for a specific site. 相似文献
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介绍了广东省台山电厂5号机组烟气脱硝工程选用液氨作为反应剂的工艺设计以及针对危险化学品液氨采取的一些具体措施,并对液氨储存区的设计提出了一些看法. 相似文献
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《Waste management & research》1997,15(4):407-427
This research examines how each of the design variables associated with the design of residential curbside recycling programs affects the participation rate, as well as the effect of interactions between the variables. The evaluation of each design variable includes a literature review and an analysis of the results of six published surveys of curbside recycling programs. The results of this research show that there is no single ideal design for residential curbside recycling programs, but that a variety of combinations of design variables have proven to be successful. This suggests that when designing a recycling program, the costs, needs and goals of the community should be significant factors while taking into consideration the effect of some design variable options on participation. Based on these results, four residential curbside recycling programs were designed: two to maximize participation rates without significant regard to cost; and the other two with the goal of achieving a balance between participation rate and program cost. 相似文献
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A disturbing trend among governmental agencies is the remediation of so‐called “nonhazardous” contaminated sediments/soils by deposition in minimum‐design Subtitle D municipal solid waste (MSW) landfills or landfills with equivalent design. This is done despite the fact that, in terms of protection of public health and environmental quality, the designation “nonhazardous” is misleading at best, and the fact that minimum‐design Subtitle D landfills as being allowed will not ensure protection of groundwater quality for as long as the buried wastes remain a threat. Although acknowledged in the regulatory documentation and exposed in the writings of a few in the scientific/engineering community, the environmental and public health issues that will inevitably be faced at minimum‐design Subtitle D landfills are underplayed, and even misrepresented, to the public. Discussion of relevant issues, as well as remarkable omissions, characterized the October 2004 United States Army Corps of Engineers (US ACE)/United States Environmental Protection Agency (US EPA)/Sediment Management Work Group (SMWG) conference,” Addressing Uncertainty and Managing Risk at Contaminated Sediment Sites.” This article addresses many of those neglected issues. © 2005 Wiley Periodicals, Inc. 相似文献
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A general theory known as the waste reduction (WAR) algorithm has been developed to describe the flow and the generation of potential environmental impact through a chemical process. The theory defines indexes that characterize the generation and the output of potential environmental impact from a process. The existing theory has been extended to include the potential environmental impact of the energy consumed in a chemical process. Energy will have both an environmental impact as well as an economic impact on process design and analysis. Including energy into the analysis of environmental impact is done by re-writing the system boundaries to include the power plant which supplies the energy being consumed by the process and incorporating the environmental effects of the power plant into the analysis. The effect of this addition on the original potential impact indexes will be discussed. An extensive engineering economic evaluation has been included in the process analysis which inherently contains the cost of the consumed energy as an operating cost. A case study is presented which includes a base process design and two modifications to the base design. Each design is analyzed from an economic perspective and an environmental impact perspective. The environmental impact analysis is partitioned into the impacts of the non-product streams and the impacts of the energy generation/consumption process. The comparisons of these analysis procedures illustrate the consequences for decision making in the design of environmentally friendly processes. 相似文献
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Sami A. Fam David M. Falatko Joseph E. Higgins Stewart Mountain Anthony J. Pirelli Michael Gaudette 《补救:环境净化治理成本、技术与工艺杂志》2012,22(4):49-74
This article describes a design approach that has been developed for bioremediation of chlorinated volatile organic compound–impacted groundwater that is based upon experience gained during the past 17 years. The projects described in the article generally involve large‐scale enhanced anaerobic dechlorination (EAD) and combined aerobic/anaerobic bioremediation techniques. Our design approach is based on three primary objectives: (1) selecting and distributing the proper additives (including bioaugmentation) within the targeted treatment zone; (2) maintaining a neutral pH (and adding alkalinity when needed); and (3) sustaining the desired conditions for a sufficient period of time for the bioremediation process to be fully completed. This design approach can be applied to both anaerobic and aerobic bioremediation systems. Site‐specific conditions of hydraulic permeability, groundwater velocity, contaminant type and concentrations, and regulatory constraints will dictate the best remedial approach and design parameters for in situ bioremediation at each site. The biggest challenges to implementing anaerobic bioremediation processes are generally the selection and delivery of a suitable electron donor and the proper distribution of the donor throughout the targeted treatment zone. For aerobic bioremediation processes, complete distribution of adequate concentrations of a suitable electron acceptor, typically oxygen or oxygen‐yielding compounds such as hydrogen peroxide, is critical. These design approaches were developed based on understanding the biological processes involved and the mechanics of groundwater flow. They have evolved based on actual applications and results from numerous sites. An EAD treatment system, based on our current design approach, typically uses alcohol as a substrate, employs groundwater recirculation to distribute additives, and has an operational period of two to four years. An aerobic in situ treatment system based on our current design approach typically uses pure oxygen or hydrogen peroxide as an electron acceptor, may involve enhancements to groundwater flow for better distribution, and generally has an operational period of one to four years. These design concepts and specific project examples are presented for 17 sites. © 2012 Wiley Periodicals, Inc. 相似文献