己二酸和己二酸钠强化石灰石WFGD的对比研究

在湍球塔设备上进行了己二酸和己二酸钠强化石灰石WFGD的对比研究,考察了2种添加剂对脱硫过程的强化和缓冲作用,分析计算了2种添加剂对石灰石的利用率。实验结果表明,2种添加剂可以在较低浆液pH下维持较高脱硫率,并且2种添加剂均促进了CaCO₃的溶解,在相同条件下己二酸钠有更好的脱硫效果,而己二酸有更好的缓冲作用,且己二酸促进CaCO₃溶解的效果更显著。     

湿法脱硫石灰石浆液密度的敏感性分析

石灰石浆液的性能是影响湿法烟气脱硫效率的主要因素,而石灰石浆液的密度又是影响其性能的主要参数。现场制浆过程中,运行参数的变动会使得浆液密度值发生变化,从而影响浆液性能。因此,通过调整制浆系统运行参数,寻找石灰石浆液密度敏感因素,对优化浆液性能具有重要意义。以某600 MW火力发电厂湿式脱硫制浆系统作为研究对象,通过现场...     

腐殖酸钠在湿法石灰石烟气脱硫系统中阻垢性能的研究

介绍了腐殖酸钠(HAS)的阻垢机理,研究了HAS在石灰石湿法烟气脱硫系统中的阻垢效应,同时在相同的条件下与己二酸的阻垢效果作了对比实验.结果表明,HAS对pH在5.5～6.5、质量分数为3.5%的石灰石脱硫浆液有很好的缓冲作用;并在此浓度的脱硫浆液中,质量浓度为1.5g/L的HAS的阻垢效果达到最佳.石灰石浆液中挂片上的结垢量对比实验得出,添加最佳浓度己二酸时的结垢量,只比添加最佳浓度HAS时的结垢量平均少1.8×10-4g/cm2.     

鼓泡塔中有机酸强化粗颗粒石灰石新型烟气脱硫

对传统石灰石湿法烟气脱硫进行了改进,提出了一种新型烟气脱硫方法,即在鼓泡塔中添加有机酸,采用大颗粒石灰石(210 μm)代替传统的细颗粒石灰石(5～20 μm)进行脱硫.实验在鼓泡搅拌吸收反应器中对比研究了新老两种脱硫工艺.结果表明,当210 μm石灰石浆液中醋酸摩尔浓度达10～30 mmol/L,其脱硫率和石灰石利用率分别为95%和93.5%,均达到甚至优于传统石灰石脱硫结果.实验研究了影响脱硫率的各种因素:添加醋酸浓度、入口SO2浓度、石灰石浆液浓度、气体停留时间以及温度等,并提出添加醋酸促进SO2吸收的机理.运用该新型烟气脱硫方法,可降低电厂的基础投资和运行费用,大大加强系统的稳定性和抗击烟气中SO2波动的能力.     

脱硫灰中杂质对石灰石脱硫活性的影响

研究脱硫灰中杂质对石灰石脱硫活性的影响具有重要意义,采用烟气湿法脱硫用石灰石粉反应速率的测定方法,使用瑞士万通902智能电位滴定仪,分析了SiO2、Al2O3、Fe2O3、CaSO3与MgO等脱硫灰中5种杂质对石灰石脱硫活性的影响。结果表明,在实验浓度范围内,SiO2、Al2O3、CaSO3的加入在一定程度上促进了石灰石的溶解,而MgO、Fe2O3的加入在一定程度上抑制了石灰石的溶解。将脱硫灰与石灰石掺合作脱硫剂时,要综合考虑这5种杂质对石灰石溶出的影响,选择适宜的脱硫灰和石灰石掺合比。     

石灰石湿法脱硫过程中SO2吸收数学模型

为揭示石灰石湿法脱硫体系中喷淋塔内SO2的浓度和脱硫效率的变化情况,针对喷淋塔内石灰石在气膜控制、气液膜控制和固体溶解控制的3个不同阶段,以双膜理论为基础,以单个石灰石颗粒为研究对象,通过石灰石在不同阶段的转化率和粒径变化,得到SO2在不同阶段脱硫效率随时间的变化规律,建立SO2吸收的数学模型.模型计算结果表明,在烟气行程上,脱硫效率受SO2气膜传质阻力和石灰石溶解速率限制.在吸收塔底部和上端SO2吸收速率较低,在SO2和石灰石摩尔比在适宜条件下,有效吸收段高度为2 m左右.理论模型揭示的规律对喷淋塔的设计和运行参数选取有一定借鉴意义.     

湿式逆流喷淋脱硫塔中SO_2吸收特性的研究

根据双模吸收理论及SO2在溶液中电离特性,建立了逆流喷淋塔的SO2吸收模型,在考虑浆液飞溅到塔壁的影响后,模拟结果与实验值吻合较好。根据吸收模型,对塔内液气比和浆液的含固率等因素进行了分析。研究表明:减少浆液飞溅到塔壁可提高浆液利用率及脱硫装置性能;根据烟气中SO2的初始浓度及最终脱硫效率,可合理选择液气比及吸收时间(塔的高度);浆液中的含固率直接影响到SO2的吸收速率、循环浆液量、脱硫效率及浆液中SO2浓度等,在液气比较小时,含固率对脱硫效率的影响尤其明显。     

湿式逆流喷淋脱硫塔中SO2吸收特性的研究

根据双模吸收理论及SO2在溶液中电离特性,建立了逆流喷淋塔的SO2吸收模型,在考虑浆液飞溅到塔壁的影响后,模拟结果与实验值吻合较好。根据吸收模型,对塔内液气比和浆液的含固率等因素进行了分析。研究表明：减少浆液飞溅到塔壁可提高浆液利用率及脱硫装置性能;根据烟气中SO2的初始浓度及最终脱硫效率,可合理选择液气比及吸收时问（塔的高度）;浆液中的含固率直接影响到SO2的吸收速率、循环浆液量、脱硫效率及浆液中SO2浓度等,在液气比较小时,含固率对脱硫效率的影响尤其明显。     

无机盐对SO2—H2O—CaCO3气液固三相反应系统pH值的影响

研究了硫酸钠、硝酸钠和氯化钠及相应钙盐对石灰石浆液烟气脱硫条件下ＳＯ２－Ｈ２Ｏ－ＣａＣＯ３气、液、固三相反应系统中ｐＨ值的影响。发现硫酸钠能明显提高系统的ｐＨ值，硝酸钠和氯化钠使ｐＨ值提高的幅度不大，而３种钙盐均使ｐＨ值降低。根据膜模型的分析结果，认为无机盐影响该反应系统ｐＨ值的主要原因是无机盐的加入改变了石灰石表面的ｐＨ值。     

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。     

Technical Description of Parameters Influencing the pH Value of Suspension Absorbent Used in Flue Gas Desulfurization Systems

Abstract

As a result of the large limestone deposits available in Poland, the low cost of reagent acquisition for the large-scale technological use and relatively well-documented processes of flue gas desulfurization (FGD) technologies based on limestone sorbent slurry, wet scrubbing desulfurization is a method of choice in Poland for flue gas treatment in energy production facilities, including power plants and industrial systems. The efficiency of FGD using the above method depends on several technological and kinetic parameters, particularly on the pH value of the sorbent (i.e., ground limestone suspended in water). Consequently, many studies in Poland and abroad address the impact of various parameters on the pH value of the sorbent suspension, such as the average diameter of sorbent particles (related to the limestone pulverization degree), sorbent quality (in terms of pure calcium carbonate [CaCO₃] content of the sorbent material), stoichiometric surfeit of CaCO₃ in relation to sulfur dioxide (SO₂) absorbed from flue gas circulating in the absorption node, time of absorption slurry retention in the absorber tank, chlorine ion concentration in sorbent slurry, and concentration of dissolved metal salts (Na, K, Mg, Fe, Al, and others). This study discusses the results of laboratory-scale tests conducted to establish the effect of the above parameters on the pH value of limestone slurry circulating in the SO₂ absorption node. On the basis of the test results, a correlation equation was postulated to help maintain the desirable pH value at the design phase of the wet FGD process. The postulated equation displays good coincidence between calculated pH values and those obtained using laboratory measurements.     

湿法烟气脱硫反应过程的实验研究

在石灰石/石膏湿法烟气脱硫中试台上,系统开展了浆液pH值、飞灰浓度、液气比、入口SO2浓度、烟气速度和氧化方式等对脱硫反应过程影响的实验研究。实验表明,脱硫效率随着石膏浆液pH值、液气比的升高而增加,且入口SO2浓度越高,液气比越低,影响效应越明显;脱硫效率随着烟气速度、烟气温度和入口SO2浓度的增加而下降;石膏浆液中飞灰含量对系统脱硫效率具有一定的促进作用:pH值>5.6,飞灰浸出液中Fe3+含量相对较低,Fe3+对脱硫反应过渡态催化氧化影响程度较轻,不同工况脱硫效率差别不大。pH值<5.6,飞灰浸出液中Fe3+含量随pH值降低而增大,增效效果逐渐显著;氧化方式对脱硫反应过程有明显的影响,强制氧化工艺的脱硫效率比自然氧化的高5%左右。     

Asbestos: Rationale Behind A Proposed Air Quality Standard

A computerized simulation model has been developed to compute energy requirements of a limestone slurry flue gas desulfurization (FGD) system as a function of FGD system design parameters, power plant characteristics, coal properties, and sulfur dioxide emission regulation. Results are illustrated for a "base case" plant of 500 MW, burning 3.5% sulfur coal, meeting the federal new source performance standard of 1.2 lb SO₂/10⁶ Btu. The flue gas is cleaned by an electrostatic precipitator followed by a limestone FGD system with a TCA scrubbing vessel and an optimized in-line steam reheater. The total FGD system energy requirement for this case was found to be 3.4% of the total energy input to the boiler. Sensitivity analyses were then performed in which the nominal values of ten system parameters were individually varied. This caused the total FGD system energy requirement to vary between 2.5 % and 6.1 % of the gross plant output for the range of parameters tested. The most sensitive parameters were found to be scrubbing slurry pH, which affects pumping requirements, and stack gas exit temperature, which affects reheat requirements. In all cases, FGD energy requirements were minimized when the SO₂ emission standard was met by partially bypassing the scrubber. In light of the recent Clean Air Act Amendments this option may not be feasible in the future.     

用于CO2捕集的Mg(OH)2粉末溶解速率

氢氧化镁是一种正在研究的用于脱除烟气中低浓度CO2的化学吸收剂。为了掌握工业用氢氧化镁粉末的溶解速率,利用缓冲溶液,在不改变溶液体积的情况下对不同悬浊液浓度、溶液温度、溶液pH值和搅拌速率情况下的氢氧化镁粉末溶解速率进行了研究。提高悬浊液浓度、提高溶液温度、降低溶液pH值和提高搅拌速率均能增大氢氧化镁的溶解速率。悬浊液浓度从0.1 mol/L增加到1 mol/L时,溶解速率增大了2.2倍;温度从23℃增加到52℃时,溶解速率增大了4.3～9.5倍;pH值从9.8降低到6.6时,溶解速率增大了78～225倍;搅拌速率从350 r/min增加到700 r/min时,溶解速率增大了1～2倍。     

用于CO2捕集的Mg（OH）2粉末溶解速率

氢氧化镁是一种正在研究的用于脱除烟气中低浓度CO2的化学吸收剂。为了掌握工业用氢氧化镁粉末的溶解速率,利用缓冲溶液,在不改变溶液体积的情况下对不同悬浊液浓度、溶液温度、溶液pH值和搅拌速率情况下的氢氧化镁粉末溶解速率进行了研究。提高悬浊液浓度、提高溶液温度、降低溶液pH值和提高搅拌速率均能增大氢氧化镁的溶解速率。悬浊液浓度从0.1 mol/L增加到1 mol/L时,溶解速率增大了2.2倍;温度从23℃增加到52℃时,溶解速率增大了4.3～9.5倍;pH值从9.8降低到6.6时,溶解速率增大了78～225倍;搅拌速率从350 r/min增加到700 r/min时,溶解速率增大了1～2倍。     

Thiosulfate as an Oxidation Inhibitor in Flue Gas Desulfurization Processes: A Review of R&D Results

Sodium thiosulfate (Na₂S₂O₃) has been tested in a pilot plant as an oxidation inhibitor in flue gas desulfurization by lime and limestone slurry scrubbing with and without MgO and adiplc acid additives. The effectiveness of thiosulfate is proportional to the inhibitor product, defined as the product of thiosulfate concentration (M), calcium concentration (M), and the moles of SO₂ absorbed per hour per liter of hold tank volume. Gypsum saturation was less than 100 percent and scaling was eliminated when the inhibitor product exceeded 0.3 × 10^?6(gmol/L)³/h. Thiosulfate was relatively more effective in systems with chlorides and less effective in systems promoted by MgO. An inhibitor product greater than 10^?6(gmol/L)³/h significantly enhanced dewatering of solids from limestone scrubbing. SO₂ removal and/or limestone utilization were increased in systems that started with less than 10 mM dissolved calcium.     

微波-Fenton对沼液中抗生素和激素的高级氧化

采用微波强化Fenton氧化处理系统,研究H2O2浓度、Fe2+浓度、初始pH、微波辐射时间和微波辐射功率对沼液中喹乙醇、土霉素、四环素及金霉素降解效果的影响.结果发现,采用微波强化Fenton氧化降解沼液中抗生素与激素的最优条件是:H2O2浓度为40 mg/L、Fe2+浓度为12 mg/L、初始pH为4、微波辐射时间为2 min、微波辐射功率为中火(445W),沼液中喹乙醇、土霉素、四环素、金霉素和COD的去除率分别达到67％、93％、91％、88％和46％.在水浴条件下,与单独微波辐射和单独Fenton相比,微波强化Fenton氧化有明显的优越性.     

Simultaneous removal of NOx,SO2, and Hg from flue gas in FGD absorber with oxidant injection (NaClO2)– full-scale investigation

ABSTRACT

This article presents the results of an industrial-scale study (on 400 MW_e lignite fired unit) of simultaneous NO_x, SO₂, and Hg^T removal in FGD absorber with oxidant injection (NaClO₂) into flue gas. It was confirmed that the injection of sodium chlorite upstream the FGD (Flue Gas Desulfurization) absorber oxidize NO to NO₂, Hg⁰ to Hg²⁺, and enhancing NO_x and Hg^T removal efficiency from exhaust gas in FGD absorber. Mercury removal efficiency grows with the rise of degree of oxidation NO to NO₂ and was limited by the phenomenon of re-emission. For NO_x removal the most critical parameters is slurry pH and temperature. There was no negative effect on sulfur dioxide removal efficiency caused by oxidant injection in tested FGD absorber. Based on the data provided, NO_x and Hg^T emissions can be reduced by adjusting the FGD absorber operating parameters combined with oxidant injection.     

The reductive degradation of 1,1,1-trichloroethane by Fe(0) in a soil slurry system

Most studies on the treatment of chlorinated contaminants by Fe(0) focus on aqueous system tests. However, few is known about the effectiveness of these tests for degrading chlorinated contaminants such as 1,1,1-trichloroethane (TCA) in soil. In this work, the reductive degradation performance of 1,1,1-TCA by Fe(0) was thoroughly investigated in a soil slurry system. The effects of various factors including acid-washed iron, the initial 1,1,1-TCA concentration, Fe(0) dosage, slurry pH, and common constituents in groundwater and soil such as Cl^?, HCO₃ ^?, SO₄ ^2?, and NO₃ ^? anions and humic acid (HA) were evaluated. The experimental results showed that 1,1,1-TCA could be effectively degraded in 12 h for an initial Fe(0) dosage of 10 g L^?1 and a soil/water mass ratio of 1:5. The soil slurry experiments showed two-stage degradation kinetics: a slow reaction in the first stage and a fast reductive degradation of 1,1,1-TCA in the second stage. The reductive degradation of 1,1,1-TCA was expedited as the mass concentration of Fe(0) increased. In addition, high pHs adversely affected the degradation of 1,1,1-TCA over a pH range of 5.4–8.0 and the reductive degradation efficiency decreased with increasing slurry pH. The initial 1,1,1-TCA concentration and the presence of Cl^? and SO₄ ^2? anions had negligible effects. HCO₃ ^? anions had a accelerative effect on 1,1,1-TCA removal, and both NO₃ ^? and HA had inhibitory effects. A Cl^? mass balance showed that the amount of Cl^? ions released into the soil slurry system during the 1,1,1-TCA degradation increased with increasing reaction time, suggesting that the main degradation mechanism of 1,1,1-TCA by Fe(0) in a soil slurry system was reductive dechlorination with 1,1-DCA as the main intermediate. In conclusion, this study provides a theoretical basis for the practical application of the remediation of contaminated sites containing chlorinated solvent.