烟气脱硫技术的应用研究

概述了国内外烟气脱硫技术的应用现状，脱硫原理及其特点，并提出了我国烟气脱硫技术的研究开发方向。     

锅炉烟气脱硫除尘一体化装置的开发与应用

本文介绍了国内外已应用的锅炉脱硫除尘一体化装置,并结合国情,提出了应重点发展的锅炉烟气脱硫除尘一体化装置。     

中国燃煤锅炉烟气脱硫技术的发展前景

本文在综述我国燃煤中小型锅炉和电站锅炉烟气脱硫技术现状的基础上,分析了我国燃煤锅炉烟气脱硫技术的发展前景．分析结果指出：我国中小型燃煤锅炉烟气脱硫技术近期是以完善湿法脱硫技术为主,远期将大力发展干法脱硫技术;在电站锅炉烟气脱硫方面,规模较小的电站锅炉将以喷雾干燥法为主要发展方向,大型电站锅炉近期仍以湿式石灰石－石膏法为主,远期将大力发展电子束辐照氨法脱硫脱硝技术。     

锅炉烟气脱硫除尘一体化装置的开发与应用

本文介绍了国内外已应用的锅炉脱硫除尘一体化装置,并结合国情,提出了应重点发展的锅炉烟气脱硫除尘一体化装置.     

锅炉烟气脱硫除尘一体化装置的开发与应用

本文介绍了国内外已应用的锅炉脱硫除尘一体化装置,并结合国情,提出了应重点发展的锅炉烟气脱硫除尘一体化装置.     

烟气脱硫技术的应用研究

概述了国内外烟气脱硫技术的应用现状、脱硫原理及其特点 ,并提出了我国烟气脱硫技术的研究开发方向     

超重力法锅炉烟气同时除尘脱硫脱硝

锅炉燃烧过程中产生的粉尘、SO2和NOx会对环境和人类造成严重的危害。随着人们环保意识的加强,锅炉烟气净化要求日趋严苛。进行了以O3为氧化剂,NaOH溶液为吸收剂,使用超重力反应器对锅炉尾气进行同时除尘脱硫脱硝的侧线实验研究,考察了不同操作条件对粉尘、SO2和NOx脱除率的影响规律,确定了适宜的操作条件：超重力反应器转速为1 000 r·min-1,气液比为125,pH值为11,O3/NOx物质的量之比为1.1。在该条件下,粉尘脱除率可达98.3%,SO2脱除率为98.4%,NOx脱除率为68.7%,处理后烟气能达标排放。超重力除尘脱硫脱硝一体化技术具有成本低、效率高、设备小和投资少等优点,在中小锅炉烟气净化过程具有广泛的应用前景。     

湿式等离子体烟气脱硫试验研究

介绍了湿式等离子体烟气脱硫试验,研究了模拟烟气参数、反应器结构和放电特性等因素对脱硫效率的影响,实验表明,试验结果为工业性应用提供了基本资料。     

锅炉烟气联合脱硫脱氮技术

硫氧化物和氮氧化物是燃煤锅炉排放的主要污染物 ,传统分步脱硫脱氮设备昂贵且效率不高 ,而联合脱硫脱氮技术具有很大的优越性 ,如可以减小系统的复杂性、具有更好的运行性能、较低的成本及较小的占地面积 ,因此实现在一个系统内同时脱硫脱氮的工艺成为国内外烟气净化技术的研究重点。对近年来国内外各种联合脱硫脱氮技术的脱除原理、研究现状、应用情况和主要优缺点进行了论述 ,并对各工艺的经济技术指标给予了多方面的比较。通过对两类烟气联合脱硫脱氮技术 (炉内联合脱除和烟气中联合脱除 )的分析、综合和比较 ,找出了我国今后脱硫脱氮技术的研究重点 ,从而为脱硫脱氮技术的进一步开发和改进提供参考     

Use of Seawater in Flue Gas Desulfurization

For seasite power plants using seawater for condenser cooling, Bechtel developed a new process to remove better than 90 percent of flue gas SO₂ using seawater and lime. Tests demonstrate that marine life is not affected by the effluent from this unique scrubbing process; therefore, the aqueous effluent containing reacted products (gypsum) in solution at low concentration is suitable for discharge to the sea.     

Modeling of Dry Injection Flue Gas Desulfurization

Dry processes for controlling sulfur dioxide emissions by injecting sodium based sorbents in the ductwork ahead of a bag filter are effective and more simple alternatives to conventional FGD processes. This paper presents a fundamental kinetic model of the dry injection process. Experimental data from pilot scale tests are reported. The model is shown to be applicable to the dry injection process. However, further experimental work is recommended to get a better understanding of the reaction mechanisms.     

喷射鼓泡法烟气脱硫工艺

对以喷射鼓泡反应器为主设备，石灰石浆液为脱硫剂的湿法烟气脱硫工艺进行了实验研究，结果表明主要参数[烟气压降Δp、ф（液气）比、吸收液pH值、进气SO2浓度]对脱硫效率均有较大的影响。     

Sulfur Gas Emissions from Flue Gas Desulfurization Sludge Ponds

This paper presents initial measurement data on the emission of volatile, reduced sulfur-containing gases from flue gas desulfurization (FGD) storage ponds. Several different types of FGD stored sludges were studied including lime, limestone, and mixtures of fly ash and lime or limestone residues, some of which had been chemically stabilized. The volatile sulfur gas emissions were cryogenically concentrated and determined by wall-coated, open-tubular capillary column gas chromatography using a flame photometric detector. Hydrogen sulfide, carbonyl sulfide, dimethyl sulfide, carbon disulfide, and an unusual, unidentified sulfur-containing compound were found in the gaseous pond flux. Benzene, toluene, and α-pinene were also identified by gas chromatography-single ion monitoring mass spectrometry. The total reduced sulfur gas emission from a 100 acre pond approximated 2.0 kg day^?1 (as sulfur).     

Resource Recovery from Flue Gas Desulfurization Systems

The cost effective benefits of yielding a flue gas desulfurization (FGD) sludge predominantly composed of CaSO₄·2H₂O, have been previously established. The recovery of this material as FGD by-product gypsum has been demonstrated abroad. Recently U.S. wallboard manufacturers have recognized the viability of this recovery practice. Such techno-economic decision making variables as a) by-product specification, b) transportation costs, and c) location of suitable FGD systems enable the recognition of FGD by-product recovery. Recent investigations of resultant solids content and chloride washing reflect the technical possibility of delivering a suitable product. Commercial and economic factors favor recovery based upon rising disposal and transportation costs. Existing and near term proposed systems surface the technical and commercial problems faced by utilities considering recovery.

Generation of an oxidized FGD sludge consisting of 90⁺% CaSO₄·2H₂O and dewatered to 80⁺% solids is technically achievable by air sparging within the FGD system. Although the product is suitable for land disposal, electric power utilities should consider and evaluate by-product recovery. U.S. wallboard manufacturers have established technical criteria for FGD by-product gypsum. Percent CaSO₄·2H₂O, final solids content, particle size, and chloride content are primarily technical parameters. Technology exists within the FGD industry to satisfy these criteria and results are discussed.

Economic factors comparing mining costs, transportation costs, and disposal costs are developed for specific utility projects. Such comparison established generalized financial criteria for a given utility to develop the economic reasonableness of considering FGD byproduct recovery.

End product user perspectives are presented providing electric utilities with a realistic appreciation for by-product recovery potential. Location of existing wallboard plants highlight potential recovery regions. Quality control problems are discussed in terms of generating a by-product rather than a disposable material.     

Status and Problems of Regenerable Flue Gas Desulfurization Processes

Fourteen sulfur and/or sulfuric acid producing regenerate FGD processes were discussed at the 1974 FGD Symposium in Atlanta. During the period elapsed since then, considerable status change has occurred on many of these regenerable processes. Other regenerable processes which were not as well known during 1974 have surfaced in 1975. The problems of obtaining reducing gases (hydrogen sulfide, carbon monoxide, and hydrogen) for the reduction of sulfur dioxide product streams to elemental sulfur have become severe due to shortages of natural gas or other petroleum based feedstock. A new sulfur producing process which employs CO and H₂ directly (rather than the H₂S required for liquid and vapor base Claus reactions) is gaining attention. This paper discusses briefly: (1) the announced status of the many regenerable FGD processes, (2) the problem of reductant gas supply, and (3) the effect on FGD processes of using coal based reducing gas instead of reformed natural gas.     

A History Of Flue Gas Desulfurization Systems Since 1850

Methods for removing sulfur dioxide (SO2) from boiler and furnace exhaust gases have been studied throughout the twentieth century. Early concepts useful for flue gas desulfurization (FGD) appear to have germinated in England circa 1850. The research during this period was motivated primarily by the quest to uncover the fundamental physical properties of substances.     

Estimating Costs of Flue Gas Desulfurization Systems for Utility Boilers

In September 1973, PEDCo-Environmental Specialists was awarded a study by the U. S. Environmental Protection Agency to evaluate the cost of controlling sulfur dioxide and particulate emissions from selected utility boilers. Since that time, PEDCo has conducted additional studies for the U. S. EPA, state and local control agencies, and private industry on the costs of control technology and the reliability of sulfur dioxide control systems. Current work includes determining the feasibility and environmental impact of converting selected utility boilers to coal-firing to conserve the nation’s gas and oil supplies. This paper presents an overview of the status and costs of flue gas desulfurization (FGD) systems, and the factors relating to the variability in costs. It is based in part upon work performed in developing detailed FGD cost estimating manuals for EPA.     

Current Status of the ADVACATE Process for Flue Gas Desulfurization

The following report discusses current bench- and pilot-plant advances in preparation of ADVAnced siliCATE (ADVACATE) calcium silicate sorbents for flue gas desulfurization. It also discusses current bench- and pilot-plant advances in sorbent preparation. Fly ash was ground in a laboratory scale grinder prior to slurring in order to decrease the slurring time needed for the sorbent to be reactive with SO₂. Reactivity of ADVACATE sorbents with SO₂ in the bench-scale reactor correlated with their surface area.

ADVACATE sorbents produced with ground fly ash were evaluated in the 50 cfm (85 m³/h) pilot plant providing 2 s duct residence time. ADVACATE sorbent was produced by slurrying ground fly ash (median particle size of 4.3 µm) with Ca(OH)₂ at the weight ratio of 3:1 at 90°C (194°F) for 3hto yield solids with 30 weight percent of initial free moisture. When this sorbent was injected into the duct with 1500 ppm SO₂ and at 11°C (20°F) approach to saturation, the measured SO₂ removal was approximately 60percent at a Ca/S stoichiometric ratio of 2. Previously, when ADVACATE sorbent was produced at 90°C (194°F) and at the same fly-ash-to-Ca(OH)₂ weight ratio using unground fly ash, removal under the same conditions in the duct was approximately 50 percent following 12 h slurring. The report presents the results of pilot-scale recycle tests at the recycle ratio of 2. Finally, the report discusses future U.S. Environmental Protection Agency plans for commercialization of ADVACATE.